HomeMy WebLinkAboutCOUNCIL - COMPLETE AGENDA - 06/11/2019 - WORK SESSIONCity of Fort Collins Page 1
Wade Troxell, Mayor Council Information Center (CIC)
Kristin Stephens, District 4, Mayor Pro Tem City Hall West
Susan Gutowsky, District 1 300 LaPorte Avenue
Julie Pignataro, District 2 Fort Collins, Colorado
Ken Summers, District 3
Ross Cunniff, District 5 Cablecast on FCTV Channel 14
Emily Gorgol, District 6 and Channel 881 on the Comcast cable system
Carrie Daggett Darin Atteberry Delynn Coldiron
City Attorney City Manager City Clerk
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City Council Work Session
June 11, 2019
6:00 PM
x CALL TO ORDER.
1. Council Priorities for 2019-2021. (staff: Kelly DiMartino, Tyler Marr; 10 minute staff presentation;
45 minute discussion)
The purpose of this item is to discuss and refine the list of Council priorities that were discussed at
the May 4, 2019 Council retreat.
2. Water Resources, Watershed, and Water Quality Protection Overview. (staff: Kevin Gertig, Carol
Webb; 15 minute presentation; 30 minute discussion)
The purpose of this item is to provide City council with an overview of certain functions of the Water
Utility, including water supply planning, watershed and water quality protection, and key partnerships
on the Poudre River.
x OTHER BUSINESS.
x ADJOURNMENT.
DATE:
STAFF:
June 11, 2019
Kelly DiMartino, Senior Assistant City Manager
WORK SESSION ITEM
City Council
SUBJECT FOR DISCUSSION
Council Priorities for 2019-2021.
EXECUTIVE SUMMARY
The purpose of this item is to discuss and refine the list of Council priorities that were discussed at the May 4,
2019 Council retreat.
GENERAL DIRECTION SOUGHT AND SPECIFIC QUESTIONS TO BE ANSWERED
1. Does Council agree with the characterization of the priorities presented?
2. Does Council have any additional clarification to add for priorities prior to a resolution coming forward?
BACKGROUND / DISCUSSION
Every two years, following a Council election, the newly seated City Council sits for a planning retreat to identify
priorities and confirm strategic direction. Priorities are identified for specific focus and action by the organization
on items that fit within the broader context of the City’s Vision, Mission, Strategic Plan and ensuring world class
service provision 24 hours a day, 365 days a year. Following the April 2, 2019 election, City Council held their
retreat over a two-day period on May 3 and 4. Through a process of priority identification and selection, Council
emerged with 20 priorities for its 2019-2021 term.
Many priorities reflect an enhanced effort of work already ongoing or a continuation of the previous Council’s
priorities. Staff has summarized what are believed to be the desired outcomes based on Council discussion at the
retreat. Following are the draft priorities and outcome statements:
x Affordable and accessible childcare
o Continue to identify barriers and needs related to increasing the supply of affordable childcare,
looking at a variety of solutions including development incentives and flexibility to ensure that
childcare is not a career and lifestyle limiting factor in Fort Collins.
x Undergrounding of electric infrastructure (transmission and distribution)
o Develop strategy to underground all electric system infrastructure within Fort Collins to improve
reliability and community aesthetics, including Platte River’s and other utilities’ transmission lines
and the remaining distribution lines owned by Light & Power.
x Low income benefits/rebates streamlining and consolidation
o Continue to simplify access to and participation in the variety of income-qualified benefits and
rebates the City offers. Explore elimination of redundant application and verification requirements
as well as potential impacts of setting a single income level which qualifies residents for all
programs.
x Equity and Inclusion
o Implement the usage of an equity lens, including staff and Council training, develop indicators
and metrics and consider a resolution regarding anti-discrimination.
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x Optimization of alleys outside of downtown
o Develop strategy for identifying, improving, and maximizing the use of alleys outside of the
downtown core, to fully utilize their potential and create opportunity through additional public
spaces and enable access for accessory dwelling units or affordable housing options.
x Equitable participation in culture and recreation programs
o Understand current state of participation in cultural and recreation programming and
subsequently make adjustments to current practices to improve equitable participation through
potentially expanded programming and targeted support.
x Mobile home park preservation and resident protections
o Develop policies/programs to preserve mobile home parks as a source of affordable housing and
enhance resident protections, particularly around issues of utility gouging and eviction.
x Neighborhood park refresh/future needs
o Complete assessment of current and future needs of neighborhood parks and explore funding
options that include private and public partnerships to secure resources for timely refresh of
parks.
x Reduce plastic pollution
o Consider local ordinances, state/federal advocacy, and expand educational efforts to reduce or
eliminate plastic pollution in Fort Collins and continue to track advances in treatment technology
for reducing or eliminating microplastics from water supplies (drinking, stormwater, wastewater,
and instream).
x Protect and enhance instream river flows
o Continue to improve and protect the ecological condition, aesthetic quality, and resiliency of the
Poudre River and its watershed/tributaries.
x Improved air quality
o Continue to reduce the impacts and prevalence of radon and ozone within the City through
regional collaboration, reduction in ground level ozone, and expanded education. Improve
understanding of microparticulates (particulate matter 2.5 microns or less in diameter) in Fort
Collins and any disparate impacts they may be influencing.
x Mitigate impacts of oil and gas encroachment into Growth Management Area
o Reduce or eliminate surface impacts of oil and gas production within the growth management
areas. Evaluate the impact and needed/desired changes as a result of Senate Bill 181 through a
robust public engagement process.
x Effective, innovative, and high-performing board
o Equip City Council with the resources, training and tools to be a highly effective, innovative, and
high-performing governing body.
x Reimagine community engagement
o Continue to improve community engagement and communication efforts to ensure policy
decisions that are informed by representative and inclusive cross section of a community that has
clear understanding of issues.
x City financial stability
o Increase understanding of revenue trends to inform revenue diversification, appropriate City fees,
and efforts to increase tax generation within Fort Collins.
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x Reimagine boards and commissions
o Better structure the board and commission system to set up success into the future, align with
Outcome Areas and allow for integrated perspectives. Explore models that allow for greater use
of ad hoc meetings, diverse stakeholders and additional community participation.
The remaining priorities need clarification prior to staff beginning to move in specific policy directions. As such,
staff is planning to bring the following priorities forward for newly scheduled work sessions to share work to date,
gain additional Council input and direction, and explore desired outcomes and possible next steps. These
priorities include:
x Strategies that create community jobs
x Small business plan
x Additional Bus Rapid Transit (BRT) corridors
x Affordable and achievable housing strategies
All of these priorities are outlined in Julia Novak’s retreat summary (Attachment 1), and staff will use this
information, as well as Work Session feedback, to populate Council’s Priority Dashboard. The Dashboard will
highlight intended outcomes and initial action steps when Council receives the first version in late June or early
July. For those priorities with clarifying work sessions needed, the intended outcomes will likely evolve over time
as the Council provides specific direction on each one.
ATTACHMENTS
1. Julia Novak Summary of Council Retreat (PDF)
2. Previous Council Priorities Dashboard, March 2019 (PDF)
3. Powerpoint Presentation (PDF)
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City of Fort Collins, Colorado
2019 Retreat
May 3 & 4, 2019
ATTACHMENT 1 1.1
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Attachment: Julia Novak Summary of Council Retreat (8030 : Council Priorities)
City of Fort Collins, Colorado Page 1
2019 Retreat Report
The Novak Consulting Group
Strengthening organizations from the inside out.
On May 3 and 4, 2019, the Fort Collins Mayor and Council held a retreat to establish a foundation for
effective governance and identify priorities for the next 12 to 24 months. The retreat was facilitated by
The Novak Consulting Group.
Day One
The first day of the retreat included the Mayor, Mayor Pro Tem, City Councilmembers, City Manager, City
Attorney, and Municipal Judge.
The Mayor started the retreat by sharing his excitement for this City Council and the work they can do
over the next two years. He shared congratulations to three new City Councilmembers and the Mayor Pro
Tem. Today is to learn about where one another is coming from and how we work with City staff. There
is an opportunity to share hopes and expectations and, ultimately, to hold one another accountable. The
better the Council works together, the better the community will be served. The City Council is unique –
we work together through City staff. We get together weekly, and we work together like a family. The
Mayor shared that the term “High Performing Community – for all” is his term and the question is, at the
end of the day, how can we make this community better – for all? How can the Council be a high
performing governing body – come together and accentuate the talents of one another to better serve
the community? At the end of the Council experience, hopefully, we have all gained knowledge and
experience and, hopefully, it develops us as individuals professionally. A high performing board works
together and individually. How can talents be tapped? We can have a high performing government. Darin
talks about how nobody believes government can be high performing, but we can in Fort Collins. That is
why we are here.
Setting the Stage and Introductions
The group then introduced themselves and shared expectations that they had for the retreat for both
Friday evening and Saturday:
x Come together as a Council – appreciate, understand, make a commitment to one another
x Develop shared priorities
x Begin the process of alignment between the City Plan – Strategic Plan and Council Priorities
x Get to know each other and what is important
x What do we have in common?
x Eager to serve with colleagues – camaraderie
x A better understanding of the backgrounds, gifts, and interests
x Stay away from “tried it before;” open to looking again, challenge assumptions
x Focus on the how
x Be willing to question why we do things
x Kick off our working relationship
x Shared expectations of how we build consensus
x Post-election learning – what you hear when knocking on doors
x Clarity – intentionally align resources around resources
x Appreciate that leadership can be lonely
x Visibility and appreciation for our 24x7x365 services the City provides
x Hear Council discussion – understand your interests
x Understand the limited resources we have
x Help one another stay balanced
x Do we need to stop doing something?
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Attachment: Julia Novak Summary of Council Retreat (8030 : Council Priorities)
City of Fort Collins, Colorado Page 2
2019 Retreat Report
The Novak Consulting Group
Strengthening organizations from the inside out.
High Performing Government – for All
The Council explored four questions relating to what it means to have a High Performing Government –
for All:
x What does it mean for City Government to be High Performing?
x What would it look like for the City to be led by a City Council committed to high performing
governance?
x What are the characteristics of a high performing community – FOR ALL?
x What should the City Council do to ensure it provides high performing governance?
What does it mean for
City Government to be
High Performing?
What would it look
like for the City to be
led by a City Council
committed to high
performing
GOVERNANCE?
Characteristics of a
high performing
community – FOR ALL
What should the City
Council DO to ensure it
provides high
performing
governance?
x Accountability – to
everyone
x SAR Process –
responsive to
resident questions
x Clear in
communication –
multiple audiences,
market
segmentation
x Always learning
and being curious
x High functioning is
a prerequisite to
high performance
x Data-driven
(informed)
innovation –
looking at things
from a new
perspective and
able to address
wicked problems
x Efficiency and ROI
x No games to halt
progress
x Outcome focused
x Focused on what
we can do for our
community
x We are committed
City of Fort Collins, Colorado Page 3
2019 Retreat Report
The Novak Consulting Group
Strengthening organizations from the inside out.
What does it mean for
City Government to be
High Performing?
What would it look
like for the City to be
led by a City Council
committed to high
performing
GOVERNANCE?
Characteristics of a
high performing
community – FOR ALL
What should the City
Council DO to ensure it
provides high
performing
governance?
x Focused on being
attractive to future
talent
x Demonstrate
progress
x Deep, authentic,
engagement with
the community
x No silos within or
outside – develop
durable
partnerships in all
sectors
The Ideal Member of the Governing Body
The Mayor and Council were asked to consider what makes an “ideal member of the Governing Body”
from three perspectives:
x What is the public looking for in a Mayor or City Councilmember?
x What is staff looking for from the Mayor and City Council?
x What are their council colleagues looking for in other members of the governing body?
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Packet Pg. 8
Attachment: Julia Novak Summary of Council Retreat (8030 : Council Priorities)
City of Fort Collins, Colorado Page 4
2019 Retreat Report
The Novak Consulting Group
Strengthening organizations from the inside out.
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Attachment: Julia Novak Summary of Council Retreat (8030 : Council Priorities)
City of Fort Collins, Colorado Page 5
2019 Retreat Report
The Novak Consulting Group
Strengthening organizations from the inside out.
Public Staff Council
x Honest
x Empathetic (x2)
x Trust
o Trusting
x Listens
o Listens to all sides
o Listens actively
o Active listener
x Persistent
x Patient
x Decisive
x Thick skinned
x Grateful
x Accountable
x Lean into public concerns
x Less agendas, more
curiosity
x Less policy solutions, more
“What’s the problem?”
x Advocate
x Courageous
x Ethical
x Out in the community
x Leader
x Can do attitude
x Transparent
x Available (x2)
x Do what I want
x Responsive (x3)
x Explains positions
x Communicates effectively
x Engages with everyone
x Compassionate
x Openness
x Open minded
x Authentic
x Sensitive
x Caring
x Work through the City
Manager
x Available
x Humorous
x Respectful (x3)
x Respectful of experience
and knowledge
x Informed
x Direct
x Efficient
x Honesty
x Appreciate competence
x Patient
x Empowers Staff
x Prescient
x Not overreaching
x Doesn’t cause extra work
City of Fort Collins, Colorado Page 6
2019 Retreat Report
The Novak Consulting Group
Strengthening organizations from the inside out.
Council Assignments
Council reviewed opportunities to serve as liaisons to Boards and Commissions. That information was
discussed on Day 1, and a summary of interest was provided on Day 2. The Council made some decisions
and will have further discussions as the official liaison and committee assignments are brought back for
adoption. The following items were discussed.
Board and Commission Assignments
x The Mayor agreed to be the interview partner for Landmark Preservation Commission and Parks
and Recreation Board rather than being the liaison.
x Emily agreed to be the interview partner for Planning and Zoning.
x Julie will talk with Ken about the Women’s Commission.
x Susan will talk to Ken about the Senior Advisory Board.
x Emily will talk to Ken about the Commission on Disability.
x Emily will be alternate for Finance Committee.
x Kristin agreed to be the alternate for the Legislative Review Board
Other Organization Assignments
x City/CSU Leadership Committee will be determined later.
x The Mayor will remain on the Forfeited Property Disposition Committee.
x Larimer County Behavioral Health Policy Council will be determined later.
x North College Urban Renewal Ad Hoc Committee – Kristin will be the Alternate.
x North College Urban Renewal Plan CAG will be Emily.
x North College MPO will be determined later.
x The Mayor will do North I-25 Coalition.
x Ross will join the Regional Water Collaboration Steering Committee.
Closing Comments
Each person shared a final word that summed up how they felt about the first evening of the retreat.
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Attachment: Julia Novak Summary of Council Retreat (8030 : Council Priorities)
City of Fort Collins, Colorado Page 7
2019 Retreat Report
The Novak Consulting Group
Strengthening organizations from the inside out.
Day Two
On the second day, the Executive Leadership Team joined the group. The Mayor kicked off the meeting
with some opening remarks then shared highlights from the evening's discussion about a high performing
Council for all, a high performing City Council, and a high performing government. The conversation was
exciting, positive, and forward moving for this City Council. A great Council will drive great governance for
our community.
Setting the Stage and Introductions
The Executive Leadership Team (ELT) was invited to share their expectations for the day. Those present
on Friday were asked to share a reflection about what was important to them about the conversation
during that part of the retreat.
Expectations
x Absorb and learn
x Get to know the new Council
x Teach about Poudre Fire Authority and how we interact with the City
x Understand new Council Priorities
x Begin establishing relationships between the Council and ELT
x Listen and learn – where do we go?
x Listen, learn – understand how to deliver on Council priorities
x Learn what people are looking for from a strategic perspective
x Cliché Clarification, i.e. what is “City as a Platform?”
x Clarity is your friend
x Continue to come together as a Council
x Long term rhythms 30-50-100 years
x Listen and learn – align our staff around your priorities
x Be present – listen deeply – learn and adapt
x Coalesce as a legislative and executive team
x Clarity of flow into our leadership system
x Curiosity – Clarity
Reflections
x New Council is excited and open
x Robust conversation and feedback
x Enjoyed getting to know Council at a personal level
x Genuine interest in what it could mean to be high performing Council
x New Council – BE CONFIDENT AND BRING YOUR GAME
x Sense of anticipation and energy – eager to dig in and do the work
x TEAM – we are in it together – Co-Creation!
x Don’t be satisfied with average!
x Set clear goals and expectations for staff
x Open – easy to talk through; we left on the same page
x Challenge assumptions
x We want to be an effective and innovative governing body
x Encouraging – will bring their best selves to the game
x Cathartic – refreshing to see how we want to work together
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Attachment: Julia Novak Summary of Council Retreat (8030 : Council Priorities)
City of Fort Collins, Colorado Page 8
2019 Retreat Report
The Novak Consulting Group
Strengthening organizations from the inside out.
Reviewing the Framework
The City Manager introduced the Strategic Plan and the organization's commitment to being accountable
to the Mayor and Council for accomplishing their shared priorities. The intent is to accomplish the
priorities in the two years this Council has to govern together.
Darin shared a drawing that depicted how the organization has evolved from responding as if everything
is a priority to a place that understands what makes Fort Collins so special. Being responsive to everything
stimulated a desire to be more strategic and develop a framework and a sense of priority for the
organization. The Baldrige Framework moved the City into a framework of being aligned and heading in
the same direction. Then the framework evolved to point toward the Vision – that clarity of Vision drives
the organization. Fort Collins has become strategic, and this meeting is an important part of the rhythm
of how things fit for the next two years.
1. The Election – Who is our Board of Directors?
2. Intentionally Onboard the Council – basics and logistics, an overview of services, tours of various
City facilities, then three specific hats the Council will wear.
i. General City
ii. Urban Renewal Authority
iii. Broadband
3. Two-Year Priorities.
4. Fall – Five-Year Strategic Plan Update – How do the first two years feed into the Strategic Plan and
re-adoption of the plan?
5. Spring (for Staff) and Summer and Fall (Council) two-year budget cycle. Putting money to the
priorities. Adopt the Budget.
6. Develop Annual Workplans.
7. Execution – operationalize the strategic plan.
The City lives a cycle of Plan – Do – Check – Act. It is a continuous improvement cycle. The two-year
cadence is very intentional. Staff is here today to be “all ears” and listen to your priorities, and we are also
professionals here to resource and support you!
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Attachment: Julia Novak Summary of Council Retreat (8030 : Council Priorities)
City of Fort Collins, Colorado Page 9
2019 Retreat Report
The Novak Consulting Group
Strengthening organizations from the inside out.
Strategic Outcome Areas
The Seven Strategic Outcome Areas have evolved over the last 10-12 years. The Two-Year Budget is
framed around the Outcome Areas (buckets). Over the years, the Council has tweaked and adjusted the
framework to reflect emerging priorities and provide further focus for the organization. The Council
considered the current framework and made adjustments:
x Economic Health
x Transportation and Mobility
o Mobility and Transportation Systems: Fort Collins provides safe, sustainable, convenient
and reliable multi-modal travel to, from, and throughout the City.
x Safe Community
x Neighborhood Livability and Social Health
o Healthy Communities: Fort Collins plans for a high-quality built environment, supports
quality, diverse neighborhoods, and fosters the social health of the community.
x Culture and Recreation
o Vibrant Community: Fort Collins celebrates our heritage and provides diverse arts,
culture, and recreation opportunities.
x Environmental Health
x High Performing Government
Individual Initiatives
Councilmembers shared their individual priorities that were organized by Strategic Outcome Area. The
Council was then provided 19 “dots” to use to identify their personal priorities, so we could gauge the
energy of the full Council. The initial list of individual initiatives are below with the number of dots received
noted in parenthesis.
Strategic Outcome Area Individual Initiatives
Economic Health x Workforce Support and Development (6)
o City workforce Commission – City partner with PSD to
create internships that lead to jobs
x Affordable, Accessible Childcare (5)
x Reviving small business development process (5)
x 100% electric distribution underground (last 1% and high voltage
lines PRPA) (4)
x Sales tax revenue enhancement strategies (2)
x Electric distribution grid more resilient for the integration of DG,
RE, EV, DERMS at Neighborhood Level (2)
x Economic Development Plan (2)
x BHAG Business/Technology for Engagement/Partnership – talent,
wealth generation for all (1)
x Refine and Review Economic Development Strategies (1)
x Innovation and Economic Prosperity partnership with CSU/BIZ (1)
x Quarterly economic reports and updates (1)
x Smart cities and broadband integration (1)
x Refine Metro District Policies
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Attachment: Julia Novak Summary of Council Retreat (8030 : Council Priorities)
City of Fort Collins, Colorado Page 10
2019 Retreat Report
The Novak Consulting Group
Strengthening organizations from the inside out.
Strategic Outcome Area Individual Initiatives
Mobility and
Transportation Systems
x BRT (5)
o Max #2 East-West
o North College BRT
x Encouraging Transfort use (understanding barriers to use (5)
x New terminal at Northern Colorado Regional Airport (2)
x Air hub service at FNL/NoCo RA (1)
x Earlier adopters AVs/EVs/UAVs Innovation Mobility (1)
x Transportation for seniors and low income – vans, buses for those
who can’t access Transfort
Safe Community x Homeless Misbehavior – threats to residents, fights, more
residents need to feel safe (2)
x Look at misdemeanor offenses for trail infractions
Healthy Communities x Affordable Housing (5)
o Land bank, land trust, mobile home park preservation
o Increase the resources for affordable housing
o Reviewing the development process for affordable housing
o Reevaluate the City down payment assistance program
o Down payment loans, using current stock, deed
restrictions, more aggressive approach
x Mobile Home Communities (5)
o Utility price gouging – quality of life standards
o Trailer Park as landowners – eliminate displacement and
provide security
o Preserving mobile home communities and protecting
residents
x Streamline low-income rebates/access (4)
x Diversity, Equity, and Inclusion (4)
o View policies and plans through this lens – CEDAW
Resolution, elimination of discrimination
x Improve Alleyways – pave and maintain (3)
x Revisit U+2 (2)
o Right size U+2 to include neighborhood improvement and
affordable housing
x Mulberry Avenue Gateway Plan I-25 to Leman (2)
x Transitional Housing/Prevention Homelessness (2)
x Resolution for Medicare for all
x Regional collaborative for affordable housing
x Livability standards – transportation, housing cost, average salary,
etc.
x 5G Issues and Impact Mitigation
Vibrant Community x Diversity of culture and recreation opportunities (5)
x Refresh old parks – make them the hub of the neighborhoods
again (by Laurel Elementary) (4)
x Arts and Culture Plan adoption and support
x Art as an economic driver strategy – night time economy, music (1)
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Attachment: Julia Novak Summary of Council Retreat (8030 : Council Priorities)
City of Fort Collins, Colorado Page 11
2019 Retreat Report
The Novak Consulting Group
Strengthening organizations from the inside out.
Strategic Outcome Area Individual Initiatives
x Sustainable parkways and medians (1)
x Include private cultural entities in City planning – recognize
symphony, opera, MoA Gallery Walk, etc. (1)
x FoCo Tree Canopy Environment
x Cultural Resource integration – telling FoCo story
Environmental Health x Plastics (4)
o Reduce single-use plastic pollution
o Single-use plastic bags – charge? Tax?
o Plastic bag/straws
x River health (4)
o Further improve river/stream health
o Poudre River Health
o Maintain flows and purity of Poudre River
x Air quality issues (4)
x Regulations to protect FC from the encroachment of gas/oil (4)
x Climate Action Plan – more buy-in from the community, more
community solar (2)
x Continue to expand open space/natural area inventory (while
there is still time)
High Performing
Government
x Professional development opportunities for Council (5)
x Reimagine community engagement (5)
o Focused roundtable information sessions
x Board and Commission Evaluation and Modification (5)
o Board/Commission Redo to align with outcomes and use
more ad hoc
x Continue to improve City financial sustainability (4)
x Regionalism for local solutions (2)
o Robust City/County Engagement and partnership – FNL,
Waste, Health
x Baldrige 2.0 – Community organizations, Council, FoCo Govt (1)
x New City Hall Complex/Campus (1)
x Why did 40% vote for the Council pay question (1)
x More effective utilization of Ch. 14
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Attachment: Julia Novak Summary of Council Retreat (8030 : Council Priorities)
City of Fort Collins, Colorado Page 12
2019 Retreat Report
The Novak Consulting Group
Strengthening organizations from the inside out.
Council Priorities
There were 11 items with five or more dots; nine with four dots and one with three dots that the Council
agreed should move forward as Council priorities. Items with five or more dots will be called Top Priorities,
four dots are High Priorities, and three dots are Other. Council then worked in small groups to refine the
initiative and define success. Some items were combined when the groups worked together. The final
initiatives presented by the groups are captured below and included as an attachment to this report. Staff
will work to refine the Council work plan further and bring the priorities back to the Council for adoption.
Strategic
Outcome Area Priority Council Priority Success
Economic
Health
Top Priority EH-1: Create Strategies that lead
to jobs for the community.
x Outcomes partnerships PSD
and FRCC
x Identify incentives
x City lead by example
x Internships
x Job placement to fill high
demand areas
Top Priority EH-2: Accessible, affordable
childcare for all.
x Increase capacity
x Identify true need – barriers
to childcare; define what the
childcare needs are that
exist in the community
x Fee waivers to incent
scholarships
x Rebates for development
fees for child care centers
x More flexible development
standards
x Childcare no longer a career
and lifestyle limiter
x Reduce barriers to entry
Top Priority EH-3: Executable plan to support
small business.
x The same level of support as
primary/key accounts
x Development/licensing
navigation
x Identify needs and gaps
x Resource awareness and
education
x Referrals to partners like
Innosphere and SBDC
High Priority EH-4: 100% Electric Distribution
underground (Last 1% and High
Voltage Lines (PRPA).
x Do as part of Connexion
x Work with PRPA
x Develop a phasing plan
x Underground replacement
strategy
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City of Fort Collins, Colorado Page 13
2019 Retreat Report
The Novak Consulting Group
Strengthening organizations from the inside out.
Strategic
Outcome Area Priority Council Priority Success
Mobility and
Transportation
Systems
Top Priority MT-1: Explore additional Bus
Rapid Transit (BRT) Corridors and
revisit transit priorities.
x Pursue transit priorities
x Pursue Federal Funding
x Mobility gap identification
x Identify barriers to use and
increase ridership
Healthy
Communities
Top Priority HC-1: Have staff explore the
following options for affordable
and achievable housing and
bring them back to Council.
x Purchase and deed
restriction
x Impact fees
x Regional partnerships
x Work with partners (CSU,
land trusts, etc.)
x Down payment assistance
x Inclusionary zoning
x Land bank strategy
x Other best practices
x Better align housing
inventory with our residents’
income levels
x Mid-year budget offer on
impact fee study
x Work session to inform
Council on what is being
worked on already
Top Priority HC-2: Develop policies to
preserve mobile home parks
(zoning, right of purchase,
purchasing the redevelopment
areas encroaching on locations,
etc.).
x Develop policies and present
them to Council
Top Priority HC-3: Quality of Life Issues in
Mobile Home Communities –
Protect residents of mobile
home parks; utility gouging;
work with eviction and
mediation.
x
High Priority HC-4: Provide an update to
Council on what is happening to
streamline low-income benefits.
Look at best practices and
City of Fort Collins, Colorado Page 14
2019 Retreat Report
The Novak Consulting Group
Strengthening organizations from the inside out.
Strategic
Outcome Area Priority Council Priority Success
Other
Priority
HC-5: Develop a plan for
opportunities for improved
alleys outside of downtown area
– placemaking, front door,
access (ADU, granny flat, etc.).
x Full utilization and potential
of alley public space
Vibrant
Community
Top Priority VC-1: Understand the current
state regarding equitable
participation in City recreation
programs. Address gaps through
specific programs or support.
Develop opportunities that
appeal to diverse populations.
Develop metrics and desired
state.
x Equitable participation in
City cultural and recreational
programs
High Priority VC-1: Complete assessment of
current and future needs for
refreshing neighborhood parks.
Develop funding options
including public and private
partnerships.
x Plan with timeline, scope,
and metrics for
neighborhood park updates
Environmental
Health
High Priority EH-1: Implement local
ordinances to programs to
address plastics under City
authority. Explore state and
federal legislative advocacy.
Educate the community about
plastic pollution – how to
reduce.
x Reduce plastic pollution
x Eliminate microplastics in
drinking water and plastics in
watersheds and other
environmental areas
High Priority EH-2: Programs to protect and
enhance in stream flow. Assess
and monitor current efforts on
stream restoration. Reduce the
impact of municipal runoff.
x Improved ecological and
aesthetic quality, along with
City of Fort Collins, Colorado Page 15
2019 Retreat Report
The Novak Consulting Group
Strengthening organizations from the inside out.
Strategic
Outcome Area Priority Council Priority Success
High Priority EH-4: Evaluate SB181 and
implications to Fort Collins.
Robust public engagement
around potential regulatory
options.
x Reduce or eliminate surface
impacts of oil and gas within
the GMA
High
Performing
Government
Top Priority HP-1: Professional Development
for Councilmembers – assess the
needs and interest of
Councilmembers. Identify areas
of overlap where staff and
Council would share mutual
benefit. Evaluate best practices.
Develop and fund a plan.
x Councilmembers equipped
at being a highly effective
and innovative board
Top Priority HP-2: Improve Public
Engagement – assess barriers to
participation in existing outreach
strategies. Measure the impact
of our effort and fill the gaps as
appropriate. Identify
opportunities to flip the model
of community engagement to
where they are and on their
time.
x Policy decisions are informed
by representative and
inclusive cross-section of
community opinion
x City Communications
accurately understood by all
Top Priority HP-3: Reimagine the Board and
Commission program.
x Align with council priorities
and strategic plan outcome
areas
x Shorter terms/term limits
x Greater use of Ad Hoc vs.
permanent commissions
x Meet as needed
x Incorporate more and
different voices
x Diversity and expand
participation
x Consider engagement
“where they are” strategies
High Priority HP-4: Continue to improve City
City of Fort Collins, Colorado Page 16
2019 Retreat Report
The Novak Consulting Group
Strengthening organizations from the inside out.
Closing
1.1
Packet Pg. 21
Attachment: Julia Novak Summary of Council Retreat (8030 : Council Priorities)
City of Fort Collins, Colorado Page 17
2019 Retreat Report
The Novak Consulting Group
Strengthening organizations from the inside out.
Attachment A: 2019-2021 Fort Collins City Council Priorities
Economic Health
EH-1: Create Strategies that lead to jobs for the community.
EH-2: Accessible, affordable childcare for all.
EH-3: Executable plan to support small business.
EH-4: 100% Electric Distribution underground (Last 1% and High Voltage Lines (PRPA).
Mobility and Transportation Systems
MT-1: Explore additional Bus Rapid Transit (BRT) Corridors and revisit transit priorities.
Healthy Communities
HC-1: Have staff explore the following options for affordable and achievable housing and bring them back
to Council.
x Purchase and deed restriction
x Impact fees
x Regional partnerships
x Work with partners (CSU, land trusts, etc.)
x Down payment assistance
x Inclusionary zoning
x Land bank strategy
x Other best practices
HC-2: Develop policies to preserve mobile home parks (zoning, right of purchase, purchasing the
redevelopment areas encroaching on locations, etc.).
HC-3: Quality of Life Issues in Mobile Home Communities – Protect residents of mobile home parks; utility
gouging; work with eviction and mediation.
HC-4: Provide an update to Council on what is happening to streamline low-income benefits. Look at best
practices and coordinate with other organizations.
HC-5: Adopt an equity lens tool for past and future decision-making including hiring, boards and
commissions, community engagement, budgeting, etc. and consider the CEDAW Resolution as part of the
Equity Lens.
HC-5: Develop a plan for opportunities for improved alleys outside of downtown area – placemaking, front
door, access (ADU, granny flat, etc.).
Vibrant Community
VC-1: Understand the current state regarding equitable participation in City recreation programs. Address
gaps through specific programs or support. Develop opportunities that appeal to diverse populations.
Develop metrics and desired state.
VC-1: Complete assessment of current and future needs for refreshing neighborhood parks. Develop
funding options including public and private partnerships.
1.1
Packet Pg. 22
Attachment: Julia Novak Summary of Council Retreat (8030 : Council Priorities)
City of Fort Collins, Colorado Page 18
2019 Retreat Report
The Novak Consulting Group
Strengthening organizations from the inside out.
Environmental Health
EH-1: Implement local ordinances to programs to address plastics under City authority. Explore state and
federal legislative advocacy. Educate the community about plastic pollution – how to reduce.
EH-2: Programs to protect and enhance in stream flow. Assess and monitor current efforts on stream
restoration. Reduce the impact of municipal runoff.
EH-3: Air Quality – Local, state, and federal advocacy. Evaluate radon working group recommendations.
Pursue further reductions of City ozone precursors. Expand community programs for ozone. Conduct
assessment of the microparticulate impact on disparate groups.
EH-4: Evaluate SB181 and implications to Fort Collins. Robust public engagement around potential
regulatory options.
High Performing Government
HP-1: Professional Development for Councilmembers – assess the needs and interest of Councilmembers.
Identify areas of overlap where staff and Council would share mutual benefit. Evaluate best practices.
Develop and fund a plan.
HP-2: Improve Public Engagement – assess barriers to participation in existing outreach strategies.
Measure the impact of our effort and fill the gaps as appropriate. Identify opportunities to flip the model
of community engagement to where they are and on their time.
HP-3: Reimagine the Board and Commission program.
HP-4: Continue to improve City Financial Sustainability.
1.1
Packet Pg. 23
Attachment: Julia Novak Summary of Council Retreat (8030 : Council Priorities)
Page 1 of 15 PROGRESS KEY 25% 50% 75% 100% March, 2019
CITY COUNCIL
INITIATIVE DASHBOARD
The purpose of this dashboard is to track the progress of priorities established during the May 2017 Council retreat. It will be
updated quarterly and included in packets to guide the scheduling of items on the 6-month planning calendar.
End of Council Term Update – As of March 18, 2019
PROGRESS
COUNCIL
RETREAT PRIORITY PURPOSE AND OUTCOMES
SERVICE
AREA ACTION PLAN
ECONOMIC HEALTH
ECONOMIC HEALTH
FOCUS - Strategic
Thinking about Fees
Purpose: Improve community
understanding of why we have fees, how
they are used, how they are calculated, and
what alternatives to fees exist
Outcomes:
x Be more strategic with fees
x Work team position paper
x Less contention on how/when fees
are updated, inputs to be included,
ultimate fee recommendations
Financial
Services
Next Council Action:
None – 2018 actions complete
Other Info:
x 2019 planned efforts
a. Step 3 of CEFs
b. Development Review
Fees
c. Wet Utility Fees
ECONOMIC HEALTH
FOCUS - Business
Retention &
Expansion (BRE)
Purpose: Enhance the ability of businesses
to succeed
Outcomes:
x Engage with the business
community to understand current
barriers and challenges to success
x Identify and coordinate resources
that support existing businesses in
the city
Maintain a mix of land uses that support the
retention and expansion of businesses
Sustainability
Services
Next Council Action:
No regular meetings or work
sessions scheduled at this time
Other Info:
x Minority Owned Business
Listening Session –
Completed (Great
Attendance)
Page 2 of 15 PROGRESS KEY 25% 50% 75% 100% March, 2019
CITY COUNCIL
INITIATIVE DASHBOARD
PROGRESS
COUNCIL
RETREAT PRIORITY PURPOSE AND OUTCOMES
SERVICE
AREA ACTION PLAN
ECONOMIC HEALTH
FOCUS - Workforce
Purpose: Address employer talent needs
and diversify employment opportunities for
residents
Outcomes:
x Close the skills gap and increase
career pathways in the community
x Create alignment between
employers, partners, and
educational institutions regarding
current and future workforce
needs
Strengthen systems for regional
collaboration - specifically related
to workforce
Sustainability
Services
Next Council Action:
No regular meetings or work
sessions scheduled at this time
Other Info:
x Working with Fort Collins
Area Chamber to support:
Talent Ambassador
Program and other
implementation steps
x Talent 2.0 Website to go
live in Q1 2019
CONNECTED
SMART CITY -
Innovation / City as a
platform
Purpose: Encourage an economic
ecosystem that fosters the development of
new and creative industry
Outcomes:
x Retain, develop, and recruit
entrepreneurs and cutting-edge
companies
x Develop and support infrastructure
that encourages entrepreneurism
and innovation
x Enhance economic diversification
by supporting industry clusters
Sustainability
Services
Next Council Action:
No regular meetings or work
sessions scheduled at this time
Other Info:
x Program evaluation and
Page 3 of 15 PROGRESS KEY 25% 50% 75% 100% March, 2019
CITY COUNCIL
INITIATIVE DASHBOARD
PROGRESS
COUNCIL
RETREAT PRIORITY PURPOSE AND OUTCOMES
SERVICE
AREA ACTION PLAN
CONNECTED
SMART CITY -
Broadband
Purpose: Encourage the development of
reliable, high speed internet services
throughout the community
Outcomes:
x Fiber to the Premise to enable
high speed symmetrical service to
all premises within the GMA
Broadband
Next Council Action:
No regular meetings or work
sessions scheduled at this time
Other Info:
x Contracts in place for
CIS/OSS, Electronics,
Design & Construction.
x Teams launched in Aug for
the CIS/OSS
implementation.
x Design Electronics work
began in Sep 2018.
x Hiring of internal staff for
both Network, Outside Plant
and MDU/Business Sales is
in progress.
x Jan 2019 start design/build
of neighborhood fiber.
x Social media accounts
launched in February –
Facebook & Twitter
x Marketing Strategy in
development.
CONNECTED
SMART CITY - Smart
City Technology and
Infrastructure
Purpose: Foster a data rich environment in
the City that allows for the following
outcomes
Outcomes:
x Increase the use of data for real
time infrastructure monitoring
x Increase access to City data sets
for cocreation possibilities
x Partner with other governments
and business to address
challenges
Information
and Employee
Services/
Page 4 of 15 PROGRESS KEY 25% 50% 75% 100% March, 2019
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INITIATIVE DASHBOARD
PROGRESS
COUNCIL
RETREAT PRIORITY PURPOSE AND OUTCOMES
SERVICE
AREA ACTION PLAN
SMALL BUSINESS
VISIBILITY
Purpose: Increase visibility of small and
medium sized businesses (SMEs) within
the community
Outcomes:
x Raise awareness of the benefits of
supporting small businesses and
the local economy
x Support the development of
emerging industries and clusters
x Understand the barriers to
success faced by small
businesses
Sustainability
Services
Next Council Action:
No regular meetings or work
sessions scheduled at this time
Other Info:
x Continue support of the
Larimer County Small
Business Development
Center ($40,000 annually)
x Working with Downtown
Business Association and
area businesses to increase
access to Sales Tax Data
x Sharing the results of the
Small Business Needs
Assessment Survey with
internal and external partners
ENVIRONMENTAL HEALTH
CITY OF FORT
COLLINS UTILITIES
AND WOODWARD
INC. WASTE TO
ENERGY PROJECT
Purpose:
Partnership with other city departments and
Woodward to design, procure, construct,
and operate 2 Co-Gen units and 1 gas
conditioning system. Once operational the
infrastructure will enable the Drake Water
Reclamation Facility to convert biogas
generated from Anaerobic Digestion to
beneficial on-site use for heat and energy
needs
Outcomes:
x Reduce the GHG emissions related to
anaerobic digestion and current flaring
of excess biogas generation
Page 5 of 15 PROGRESS KEY 25% 50% 75% 100% March, 2019
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INITIATIVE DASHBOARD
PROGRESS
COUNCIL
RETREAT PRIORITY PURPOSE AND OUTCOMES
SERVICE
AREA ACTION PLAN
PRESCRIPTION
DRUG TAKEBACK
PROGRAM
Purpose: Provide opportunities to safely
dispose of prescription and over-the-
counter-drugs
Outcomes:
x Explore partnership with UC
Health
x Protect water quality by avoiding
dumping
Reduce presence of expired/unneeded
prescription and over-the-counter drugs
Police
Services/ City
Manager’s
Office / Utilities
Next Council Action:
No regular meetings or work
sessions scheduled at this time
Other Info:
x Daily drop-off location
continues at FCPS
x 2nd 2018 event held on
October 27 collected 208
pounds of drugs
x Total between kiosk and
event equaled 1432 pounds
of drugs collected
x The next takeback event is
scheduled for April 27, 2019
PLATTE RIVER
POWER AUTHORITY
AND FORT COLLINS
UTILITIES ENERGY
FUTURES –
Customer Requests
for 100% Renewable
Energy
Purpose: Offer customers the ability to
procure 100% renewable portfolio options
that Fort Collins Utilities can deliver with our
generation provider Platte River Power
Authority
Outcomes:
x Create options for customers who want
to have 100% renewable energy
delivery
Utilities
Next Council Action:
Update will be provided with the
Climate Action Plan update
Page 6 of 15 PROGRESS KEY 25% 50% 75% 100% March, 2019
CITY COUNCIL
INITIATIVE DASHBOARD
PROGRESS
COUNCIL
RETREAT PRIORITY PURPOSE AND OUTCOMES
SERVICE
AREA ACTION PLAN
PLATTE RIVER
POWER AUTHORITY
AND FORT COLLINS
UTILITIES ENERGY
FUTURES -
Integrated Resource
Plan
Purpose: Coordinate with Platte River
Power Authority the transition to generation
that meets the Climate Action Plan goals
Outcomes:
x Achieve the City’s 2020 climate
action goals identified in 2020,
2030 and 2050
Ensure key shareholders and public are
engaged
Utilities
Next Council Action:
Update will be provided with the
Climate Action Plan update
scheduled at the June 25 Work
Session
Other Info:
x Platte River plans to
complete their IRP in 2020
one year ahead of the
regularly scheduled due date
of 2021
x Platte River will seek
approval from Western Area
Power Authority (WAPA) for
an out-of cadence IRP
submission
x Platte River hosted public
meeting October 25 to kick-
off the IRP process for public
engagement with Utilities
staff
x Staff is coordinating with
Platte River on a range of
sub-tasks, such as the
demand side management
potential study.
AIR QUALITY
ISSUES - Radon
Purpose: Protect human health
Outcomes:
x Increase mitigation of high radon
levels
Sustainability
Services
Next Council Action:
Page 7 of 15 PROGRESS KEY 25% 50% 75% 100% March, 2019
CITY COUNCIL
INITIATIVE DASHBOARD
PROGRESS
COUNCIL
RETREAT PRIORITY PURPOSE AND OUTCOMES
SERVICE
AREA ACTION PLAN
AIR QUALITY
ISSUES – Outdoor
Burning
Purpose: Protect human health and
reduce nuisance from outdoor wood smoke
Outcomes:
x Implement Council direction
regarding residential outdoor
burning
Sustainability
Services
Next Council Action:
March 19th Council Session
scheduled for final consideration
of:
x Nuisance Code updates
x Appropriation of resources
for implementation and
enforcement
Other Info:
x Received Council support for
public engagement plan in
February 2018
x Policy research and public
engagement was conducted
in 2018
x Received Council feedback
to update nuisance code at
February 2019 Work
Session
Ongoing
AIR QUALITY
ISSUES - Ozone
Purpose: Protect human and
environmental health by reducing ozone
precursor emissions
Outcomes:
x Reduce ozone precursor
emissions
x Lead by example in reducing
ozone precursor emission from
lawn and garden equipment and
other sources
Sustainability
Services
Next Council Action:
No regular meetings or work
sessions scheduled at this time
Other Info:
x Update Air Quality Plan in
2018/2019, including
addressing ozone emissions
Page 8 of 15 PROGRESS KEY 25% 50% 75% 100% March, 2019
CITY COUNCIL
INITIATIVE DASHBOARD
PROGRESS
COUNCIL
RETREAT PRIORITY PURPOSE AND OUTCOMES
SERVICE
AREA ACTION PLAN
CONTINUED
PROGRESS ON
CLIMATE ACTION
PLAN
Purpose: Leverage efficiency and
innovation to accelerate the transition to a
clean energy economy and protect Fort
Collins’ quality of life and climate.
Outcomes:
x Achieve the City’s 2020 climate
action goal (20% below 2005) and
long-term (2050) carbon neutrality
goals.
Increased community (business,
resident, and academic)
engagement in achieving the
goals.
Sustainability
Services
Next Council Action:
Climate Action Plan update
scheduled for June 25 Work
Session
Other Info:
x 2019-2020 will focus on
Climate Action Plan update;
plan update will be in
partnership with the Energy
Policy and Road to Zero
Waste update and
incorporate mitigation,
resilience/adaptation and
equity lenses.
x Currently conducting
outreach to develop the
plan’s scope.
x Will launch 2019 messaging
campaign at Earth Day, April
22.
SAFE COMMUNITY
EXPAND
COMMUNITY
POLICING
Purpose: Expand Community Policing to
increase public safety and public trust
outcomes
Outcomes:
Open and operationalize a collaborative,
shared space to be used by City and CSU
departments
Police Services
Next Council Action:
Page 9 of 15 PROGRESS KEY 25% 50% 75% 100% March, 2019
CITY COUNCIL
INITIATIVE DASHBOARD
PROGRESS
COUNCIL
RETREAT PRIORITY PURPOSE AND OUTCOMES
SERVICE
AREA ACTION PLAN
Ongoing
COMMUNITY TRUST
IN POLICING
POLICY
(COMMUNITY
TRUST INITIATIVE)
Purpose: Gather information and conduct
analysis of community-proposed
Community Trust Ordinance
Outcomes:
x Review of proposed Community
Trust Ordinance
x Review of existing policies
x Historical review and comparison
x Difference between a Sanctuary
City designation and proposed
Community Trust Ordinance
x Other city research
x Options for modifications of
existing City policies or laws
x Process to report policy violations
x Community outreach process/plan
Sustainability
Services/
Police Services
Next Council Action:
No regular meetings or work
sessions scheduled at this time
Other Info:
x Community Trust
Stakeholder Group
concluded regular
meetings. Met with new
Police Chief in Sept. 2018
x Report provided to Council
in late May 2018, detailing
work to date, stakeholder
views, and planned or
continuing staff actions
x Established police-
community group for
cooperative discussion -
training events
x Partnering with City Service
Areas and NGO’s to align
missions and focus efforts
with homeless/transient
populations
x Police recruiters continue to
attend La Familia cookouts
x Most relevant police policies
translated into Spanish and
Page 10 of 15 PROGRESS KEY 25% 50% 75% 100% March, 2019
CITY COUNCIL
INITIATIVE DASHBOARD
PROGRESS
COUNCIL
RETREAT PRIORITY PURPOSE AND OUTCOMES
SERVICE
AREA ACTION PLAN
RESIDENTIAL
PARKING PERMIT
PROGRAM AND
CSU PARKING
IMPACTS
Purpose: Review and amend existing RP3
program
Outcomes:
x Ensure program is being
implemented as intended
Planning,
Development,
and
Transportation
Next Council Action:
No regular meetings or work
sessions scheduled at this time
Other Info:
x Staff recommended a new
fee policy regarding
nonresidential RP3 permits
primarily for schools and
some existing businesses
within the RP3 zones
x Staff provided the new
permit fee per
administrative policy to the
City Manager for
authorization in September
EXPAND IGA
DISCUSSION TO
USE OF HUGHES
STADIUM
Purpose: Engage CSU in a discussion on
the use of Hughes Stadium. Suggest a
community conversation with the County,
CSU, residents, and the City
Outcomes:
x Help CSU engage in a community
discussion about future uses of the
stadium site
Planning,
Development,
and
Transportation
Next Council Action:
No further Council Action
planned
Other Info:
x CSU has contracted with
CalAtlantic Homes of
Colorado (LENNAR
Page 11 of 15 PROGRESS KEY 25% 50% 75% 100% March, 2019
CITY COUNCIL
INITIATIVE DASHBOARD
PROGRESS
COUNCIL
RETREAT PRIORITY PURPOSE AND OUTCOMES
SERVICE
AREA ACTION PLAN
SMOKING IN OLD
TOWN
Purpose: Evaluate effectiveness and
changes related to existing smoking
ordinance
Outcomes:
x Reevaluate geographic boundary
x Look at enforcement methods
x Examine dedicated smoking
locations
x Make any Ordinance Amendments
as desired
Planning,
Development,
and
Transportation
Next Council Action:
No further Council action
planned.
Other Info:
x Council made a
modification to the penalty
associated with violating
the smoking ordinance in
December
x Council received a memo in
January with staff’s
recommendation to not
change the Smoke-Free-
Zone perimeter to include
Library Park
LANDBANK
PROPERTY
RFP OWNERSHIP
Purpose: Update Land Bank policy and
successfully deploy another land bank
property
Outcomes:
x Produce more affordable housing
units by selling existing parcels to
development partner(s)
x Use sales proceeds to purchase
additional land bank parcels
x Maximize the development
potential of the Land Bank
program through identifying new
resources and incentives
Sustainability
Services
Next Council Action:
No regular meetings or work
sessions scheduled at this time
Page 12 of 15 PROGRESS KEY 25% 50% 75% 100% March, 2019
CITY COUNCIL
INITIATIVE DASHBOARD
PROGRESS
COUNCIL
RETREAT PRIORITY PURPOSE AND OUTCOMES
SERVICE
AREA ACTION PLAN
UTILITY /
EFFICIENCY
PROGRAMS FOR
LOW INCOME
FAMILIES &
INDIVIDUALS
Purpose: Ensure low income segment is
supported for utility bill, conservation and
efficiency services and programs, which
also includes renewable offerings
Outcomes:
x User-friendly resources that
support utility bill assistance
x Outreach that brings materials and
awareness on support for
efficiency and conservation
improvements
x Manage opportunities for low
income to participate in renewable
energy offerings
Utilities/
Sustainability
Services
Next Council Action:
No further Council Action
planned after “Good News”
update at Feb. 5 City Council
meeting.
Other Info:
x Utilities Affordability Portfolio
with the Income Qualified
Assistance Program (IQAP)
launched on Oct. 1, 2018
x Completed IQAP application
process with 829
applications received.
Largest low-income
enrollment for a Utilities
program.
x Continuous enrollment
initiated in 2019.
CULTURE & RECREATION
ARTS, CULTURE &
MUSEUM
INTEGRATION
Purpose: Explore opportunities to leverage
City resources through community
partnerships and collaboration
Outcomes:
x Promote opportunities for
interaction between local
museums and cultural institutions.
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INITIATIVE DASHBOARD
PROGRESS
COUNCIL
RETREAT PRIORITY PURPOSE AND OUTCOMES
SERVICE
AREA ACTION PLAN
TRANSPORTATION & MOBILITY
Prioritization
model
complete
COMPLETE
SIDEWALK
PROGRAM FOR
PUBLIC SAFETY
Purpose: Update City sidewalk
prioritization model to improve public safety
and enhance safe routes to school
Outcomes:
x Make needed improvements near
Lincoln Middle School and Poudre
High School.
x Produce new prioritization model
for sidewalks
Planning,
Development,
&
Transportation
Next Council Action:
No further Council Action
planned
Other Info:
x City staff updated the
citywide sidewalk
prioritization model to
include equity and safety to
give a higher weight to
arterial sidewalk needs
ongoing
COUNTY
ENGAGEMENT FOR
BUILDING
INFRASTRUCTURE
IN CITY GMA
Purpose: Engage Larimer County in
discussion about assistance for building
infrastructure and programming within the
City’s GMA
Outcomes:
Gain County assistance in funding:
x Sidewalks
x Streets
x Bike trails
x Neighborhood Issues
Planning,
Development,
and
Transportation
/ Financial
Page 14 of 15 PROGRESS KEY 25% 50% 75% 100% March, 2019
CITY COUNCIL
INITIATIVE DASHBOARD
PROGRESS
COUNCIL
RETREAT PRIORITY PURPOSE AND OUTCOMES
SERVICE
AREA ACTION PLAN
NORTH COLLEGE
BUS RAPID
TRANSIT
Purpose:
Short Term- Provide enhanced transit
service as an interim solution to meet
transit demand needs on the North College
corridor.
Long Term - Determine feasibility, plan
and implement a North College Bus Rapid
Transit service.
Outcomes:
Short Term
x Improve transit access, connectivity
to the transit system and higher
frequencies of service to our riders
with trips on the North College
corridor
x Collect ridership and other data to
augment the planning efforts for
long term BRT goals on North
College
Long Term
x Implement a bus rapid transit
system for North College
Planning,
Development,
&
Transportation
Next Council Action:
No further Council action
planned.
Other Info:
x Staff has prepared a service
improvement option for BFO
2019-20
x BFO offer not funded.
HIGH PERFORMING GOVERNMENT
REPRIORITIZE CITY
PLAN
Purpose: Identify what’s working well
within the existing City Plan in order to
focus staff and Council resources on areas
which need addressed
Outcomes:
Adjust scope and resource of City Plan to
focus on identified needs.
Planning,
Development,
&
Transportation
Next Council Action:
Page 15 of 15 PROGRESS KEY 25% 50% 75% 100% March, 2019
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INITIATIVE DASHBOARD
PROGRESS
COUNCIL
RETREAT PRIORITY PURPOSE AND OUTCOMES
SERVICE
AREA ACTION PLAN
REIMAGINE
COMMUNITY
ENGAGEMENT
Purpose: Enhance overall community
engagement efforts and strengthen
organizational capacity for effective public
engagement
Outcomes:
x Systematic use of public
engagement framework and
planning tools
x Leverage new tools and
technology to increase
engagement with all segments of
the community, with additional
focus on underserved populations
x Use data to evaluate and improve
public engagement efforts
Information
and Employee
Services
Next Council Action:
No regular meetings or work
sessions scheduled at this time
Other Info:
x The City has updated
the engagement
spectrum to illustrate
the progression and
reciprocal nature of
public engagement.
This and additional tools
also emphasize the
community’s two largest
stakeholder groups,
businesses and
residents. Quarterly
training & development
opportunities will
enhance and equip
internal public
engagement capacity
and capability.
x Internal resources and
collaboration continue to
grow. The new Public
Engagement
Collaboration Team
works to align efforts
and outreach to plan
more effective outreach
both online and on-the-
June 11, 2019
City Council Priorities
ATTACHMENT 3 1.3
Packet Pg. 39
Attachment: Powerpoint Presentation (8030 : Council Priorities)
Direction Sought
1. Does Council agree with the characterization of the priorities as
presented?
2. Does Council have any additional clarification to add for
priorities prior to a resolution coming forward?
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Attachment: Powerpoint Presentation (8030 : Council Priorities)
Council-Term Planning Timeline
3
BFO Programs & Initiatives
EXECUTION PLANNING
Strategic Plan
BFO
2021/2022
ELECTIONS
On Board/
Retreat
2019
BFO Programs & Initiatives
2020 2021 2022
2019 Budget 2020 Budget 2021 2022
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Attachment: Powerpoint Presentation (8030 : Council Priorities)
Priorities
4
• Adopted formally by Resolution
• Provide specific focus and action within context of vision and mission
• Progress reported quarterly through Dashboard
• Strategic plan, budget offers, Council or administrative action
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Attachment: Powerpoint Presentation (8030 : Council Priorities)
Priorities By Outcome Area
Neighborhood Livability & Social
Health
1. Affordable and achievable
housing strategies
2. Mobile home park preservation
and resident protections
3. Equity and inclusion
4. Low income benefits/rebates
streamlining and consolidation
5. Optimization of alleys outside
of downtown
Economic Health
1. Strategies that create
community jobs
2. Affordable and accessible
childcare
3. Small business plan
4. Undergrounding of electric
infrastructure (transmission and
distribution)
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Attachment: Powerpoint Presentation (8030 : Council Priorities)
Priorities By Outcome Area
Transportation
1. Additional Bus Rapid
Transit (BRT) corridors
Culture and Recreation
1. Equitable participation in
culture and recreation
programs
2. Neighborhood park
refresh/future needs
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Attachment: Powerpoint Presentation (8030 : Council Priorities)
Priorities By Outcome Area
Environmental Health
1. Reduce plastic pollution
2. Protect and enhance instream
river flows
3. Improved air quality
4. Mitigate impacts of oil and
gas encroachment into
Growth Management Area
High Performing Government
1. Effective, innovative, and
high-performing board
2. Reimagine community
engagement
3. City financial sustainability
4. Reimagine boards and
commissions
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Attachment: Powerpoint Presentation (8030 : Council Priorities)
Next Steps
• Resolution consideration of all priorities on July 2
• Work sessions to clarify outcomes on:
• Strategies that create community jobs
• Small business plan
• Additional Bus Rapid Transit (BRT) corridors
• Affordable and achievable housing strategies
• Dashboard reporting starting this summer
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Attachment: Powerpoint Presentation (8030 : Council Priorities)
Direction Sought
1. Does Council agree with the characterization of the priorities as
presented?
2. Does Council have any additional clarification to add for
priorities prior to a resolution coming forward?
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Attachment: Powerpoint Presentation (8030 : Council Priorities)
DATE:
STAFF:
June 11, 2019
Carol Webb, Deputy Director, Utilities
Kevin Gertig, Utilities Executive Director
WORK SESSION ITEM
City Council
SUBJECT FOR DISCUSSION
Water Resources, Watershed, and Water Quality Protection Overview.
EXECUTIVE SUMMARY
The purpose of this item is to provide City council with an overview of certain functions of the Water Utility,
including water supply planning, watershed and water quality protection, and key partnerships on the Poudre
River.
GENERAL DIRECTION SOUGHT AND SPECIFIC QUESTIONS TO BE ANSWERED
Staff is not seeking direction from Council at this time regarding specific projects but would appreciate input on
any information provided.
BACKGROUND / DISCUSSION
About the Water Utility
The City owns and operates the Water Utility, which is part of Fort Collins Utilities. The Water Utility provides a
diverse portfolio of services and programs to its customers while supporting key outcomes for the City. The Water
Utility provides reliable, high quality water service to approximately 35,000 customer accounts (32,000 residential
and 3,000 commercial) and distributes about 8 billion gallons of treated water annually through over 500 miles of
water mains. The Water Utility generated $40.6 million in revenue in 2018. 2018 operating expenses were $20.2
million. Capital expenditures range from an average of $10 million to $15 million annually.
The Water Utility serves approximately 73% of the residents within the City’s Growth Management Area (GMA).
Fort Collins-Loveland Water District (FCLWD) provides water service for about 17% of Fort Collins residents in
the southeast portion of the GMA, while East Larimer County Water District (ELCO) serves about 8% of Fort
Collins residents in the northeast portion of the GMA. (Attachment 1)
From the source of our water supplies on the Cache la Poudre River (“Poudre River”) and Horsetooth Reservoir
to the customer tap, the Water Utility ensures that customers are provided with a reliable supply of high-quality
treated water. The Water Utility consists of many functions needed to provide a high level of service. This agenda
item will focus on programs and services related specifically to water supply planning, watershed and water
quality protection, and key partnerships to protect and enhance the Poudre River. Other functions, such as water
conservation, finance, water distribution and engineering will not be addressed in this presentation, however,
warrant a future discussion by City Council.
WATER SUPPLY PLANNING
Water Supplies and Demands
The Water Utility utilizes two main sources of water supply: the Poudre River and the Colorado-Big Thompson
(CBT) Project, which includes Horsetooth Reservoir. On average, the Water Utility treats and supplies to
customers about 24,000 acre-feet of water annually split about equally from these two sources. In addition to
treated water, the Water Utility provides about 3,000 acre-feet per year of untreated (raw) water for irrigation of
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City parks, golf courses, cemeteries, and other green belt areas. For reference, one acre-foot of water will supply
on average about 3.5 homes with water for one year.
Water Rights
In order to provide a reliable water supply, the Water Utility has acquired water rights and cash-in-lieu (CIL) of
those water rights over many decades. The Water Utility owns a diverse portfolio of water rights from the Poudre
River and its tributaries. The Water Utility also owns contractual “units” in the CBT Project, which is administered
by the Northern Colorado Water Conservancy District (Northern Water), which entitles the City to deliveries of
water from Horsetooth Reservoir. Water in the CBT Project originates from the Colorado River basin, near
Granby.
The City’s current water rights portfolio, valued at over $2 billion, yields in wet years more water than needed by
the Water Utility customers. However, these water rights yield much less in drought years and most of the yield in
good years cannot be stored or used by Water Utility customers due to the relatively small amount of water
storage capacity available to the Water Utility.
The acquisition of water rights and CIL of water rights currently occur primarily through the Water Utility’s “Water
Supply Requirements” (WSR), a fee assessed on new developments (or redevelopment) in the Water Utility water
service area. WSR ensure that adequate water supply and associated infrastructure (e.g. raw water storage) are
available to serve the development’s water needs.
City Council adopted changes to the WSR and the CIL value that became effective in 2018, moving primarily to a
“cash-focused” system. The updated policy enables the Water Utility to collect adequate funds to develop water
storage and other infrastructure and to acquire the appropriate water rights to serve future customers. The current
CIL value per acre-foot of WSR is $17,300. This translates to about $9,300 per typical single-family home or
$39,200 per 1-inch commercial tap. The CIL rate is proposed to increase to $21,500 per acre-foot of WSR in the
coming year, due mainly to increased costs for the Halligan Water Supply Project. This proposed increase will be
considered for adoption by City Council this fall. Even with this increase, the Water Utility’s CIL rate is one of the
most affordable CIL rates in the region.
WATER STORAGE, TRANSMISSION, AND DISTRIBUTION
Joe Wright Reservoir
Joe Wright Reservoir is the only storage reservoir fully owned and operated by the Water Utility available for
treated water purposes. Located near Cameron Pass on a tributary to the Poudre River, this reservoir has an
active capacity of about 7,100 acre-feet and provides water to the Water Utility’s Water Treatment Facility via the
Poudre River through two pipelines that divert off the Poudre River near Gateway Natural Area.
Horsetooth Reservoir
The Water Utility owns 18,855 units in the CBT Project, which are delivered to Utilities out of Horsetooth
Reservoir (administered by Northern Water). Northern Water has policies that limit the Water Utility’s ability to
store excess water in Horsetooth Reservoir for use in later years.
The Halligan Water Supply Project
The Water Utility is currently pursuing an enlargement of Halligan Reservoir to meet future water demands and
improve water service reliability for current customers. Halligan Reservoir has a current capacity of approximately
6,400 acre-feet and is located northwest of Livermore, 24 miles upstream of the confluence of the North Fork with
the mainstem of the Poudre River at Gateway Natural Area. The Halligan Project consists of raising the existing
Halligan Dam by approximately 25 feet to increase reservoir capacity by 8,125 acre-feet to a total of about 14,525
acre-feet. Water in the existing Halligan Reservoir is currently used and operated by the North Poudre Irrigation
Company (NPIC). After the enlargement of Halligan Reservoir, NPIC will continue to use and operate 6,400-acre
foot of capacity in the reservoir.
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(Attachment 2) is graphic depicting the location of the City’s available water storage.
Before Halligan Reservoir can be enlarged, the City must receive federal, state and local permits. The U.S. Army
Corps of Engineers (Corps) is the lead permitting agency and is currently conducting an environmental analysis of
the Project that considers and discloses to the public the analysis of potential environmental impacts of the
proposed Halligan enlargement and several alternatives to the Halligan enlargement that would also meet the
Water Utility’s needs for the project. The Halligan Water Supply Project has been in permitting since 2006. A
summary of the environmental analysis, known as the Draft Environmental Impact Statement (DEIS), is expected
to be released by the Corps in late 2019. (Attachment 3)
Water Supply and Demand Management Policy
The Water Supply and Demand Management Policy is the governing policy (Attachment 4) adopted by City
Council to direct the acquisition, development, and management of the City’s and the Water Utility’s water
supplies. The current policy was adopted in 2012 and contains guiding principles and criteria related to water
efficiency and demand management, water supply reliability, treated and raw water quality, use of surplus raw
water supplies, and regional cooperation on water resources issues. A Budgeting for Outcomes (BFO) offer was
funded in the 2019/2020 BFO process to update the Policy to reflect current conditions and to incorporate findings
of the Water Supply Vulnerability Study (see next section).
Water Supply Vulnerability Study
The Water Supply Vulnerability Study, funded in the 2017/2018 BFO process, investigated impacts to our ability
to meet water demands from changing hydrology due to a warming climate; from water supply disruptions, such
as infrastructure failures or wildfire impacts; and from changing demands due to populations shifts, land use
changes, and altered demand patterns. Through the course of the Study, the Utilities Water Resources Division
has updated its modeling systems, developed climate-altered hydrologies to capture future climate uncertainties,
developed future demand estimates around proposed City Plan growth scenarios, and developed new tools to
facilitate such a large-scale analysis. Study completion is expected by June 30, 2019. Current findings include:
x Climate is a critical driver for water supply reliability, resilience, and vulnerability (collectively called “system
performance”).
x Without the Halligan Reservoir enlargement, system performance is reduced under most future conditions.
x Long-term reductions in CBT Project water supplies due to shortages in the Colorado River system is a top
vulnerability to the Water Utility and its ability to provide a reliable water supply.
x The Water Utility now has a modeling system that can be used in the future to evaluate other risks and water
supply alternatives.
Findings of this study will serve as the foundation for the next phase of planning, which includes an update of the
Water Supply and Demand Management Policy and determination of goals related to system performance
(reliability, resilience, and vulnerability) as well as mitigation strategies to achieve those goals.
Water Distribution
Fort Collins Utilities maintains and operates over 550 miles of pipeline within the distribution system. There over
12 miles of pipe that is 100 years old or greater and over 21 miles of pipe that rate as poor or very poor by the
Water Distribution System Renewal Master Plan. These rankings are based upon ability of fire hydrants to meet
fire flow requirements, age of pipe, number of breaks, service to critical facilities as well as other criteria.
Currently the Water Utility construction crews replace approximately 2 miles of pipe in the distribution system per
year where main breaks are a problem. This is generally in the portion of town where development occurred in
the late 70s and early 80s. Construction methods during that time did not adequately protect the ductile and cast-
iron pipe from corrosive soils which is the cause of most main breaks. Compared to national benchmarks, the
City does experience a higher rate of water main breaks per hundred miles than average. These breaks interrupt
customer service and impact operating costs to the Utility.
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The Capital Construction Team has been addressing aging pipe in the Old Town area over the past few years,
including the Walnut Street and Old Town Library Projects. At the current renewal rate, pipe in the distribution
system would need to serve for 200-250 years prior to renewal. Since the useful age of pipe, especially cast iron
and ductile iron pipe, is 80-100 years; FCU is evaluating means to increase the rate of renewal of the distribution
system to assure delivery of high-quality water service.
WATERSHED AND WATER QUALITY PROTECTION
Source Watersheds
As mentioned above, the Water Utility receives its water supplies from two primary watersheds - the Cache la
Poudre River watershed and the combined Colorado and Big Thompson River Watersheds (which is where key
CBT Project infrastructure like Horsetooth Reservoir is located). Combined, the watersheds encompass
approximately 1,600 square miles of primarily forested, mountainous terrain. Concentrated development
upstream is limited to the areas around Grand Lake and Estes Park.
Unlike many other water utilities, the City owns less than 1% of the land area in its watersheds. Rather, the land is
owned and managed by a mix of federal, state, county and private landowners, and therefore, monitoring and
managing risks to water supplies requires the City to work collaboratively and in many instances across
jurisdictional boundaries to implement watershed protection projects. (Attachment 5)
Source Water Protection
Fort Collins Source Water Protection Plan (SWPP)
In 2016, Utilities Watershed Program in cooperation with the Colorado Rural Water Association and the Colorado
Department of Health & Environment completed the City’s first Source Water Protection Plan. This planning
document provides a roadmap for managing potential sources of contamination to the Water Utility’s water
supplies that are treated and delivered to customers. Through this effort, the top risk to our water supply was
identified as wildfires.
Watershed Restoration and Forest Fuels Management
Since 2013, the Water Utility has funded a reserved seat on the Board of Directors for the Coalition for the Poudre
River Watershed (CPRW). This organization was formed after the 2012 wildfires to coordinate response and
recovery activities among community non-profits, water utilities, private landowners and other community
stakeholders.
In 2016, CPRW produced a Poudre River Watershed Resiliency Plan, which identifies priority watershed areas
currently at highest risk from wildfires as well as remaining post-High Park Fire restoration needs. In 2017, the
Water Utility committed $80,000 per year to fund watershed protection projects that mitigate risks in these priority
areas. By working with CPRW and other partners, Water Utility funds are leveraged for greater impact, as they
can be used as a match to secure additional funding for wildfire hazard mitigation projects.
In 2017, Watershed Program collaborated with CPRW, the U.S. Forest Service, and other partners to identify
potential fuels reduction projects that will mitigate risks associated with large scale catastrophic wildfires in the
Poudre basin and protect water quality in the Poudre River and Horsetooth Reservoir. Hazard fuels reduction
around critical infrastructure in the watershed, such as Horsetooth and Joe Wright Reservoirs, Michigan Ditch and
the Poudre intake facility, will receive highest priority.
Source Water Spill Response Plan
Developed for Upper Poudre River in 2019, the Source Water Spill Response Plan identifies chemical hazards to
drinking water supplies that exist within the watershed and the Highway 14 corridor. This tool provides guidance
for responding to chemical spills, including notification and communication procedures along with response
actions and mitigation strategies.
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The Response Plan is a partnership between the City and the many parties who respond to and/or are impacted
by chemical spills, including first responders, downstream water users, and regulatory authorities who direct the
final cleanup.
WATER QUALITY MONITORING PROGRAMS & RIVER HEALTH
Upper Cache la Poudre River Collaborative Water Quality Monitoring Program
Since 2007, Fort Collins Utilities, City of Greeley and the Soldier Canyon Water Treatment Authority (a
governmental entity created for water treatment by ELCO, FCLWD, and North Weld County Water District) have
partnered on a cooperative water quality monitoring program, designed to track trends in river water quality in
order to anticipate future needs of the parties’ respective drinking water treatment operations. For example,
monitoring data shows that increases in many constituents observed following 2012 wildfires were short-lived and
that water quality in the Poudre River has largely returned to pre-fire condition. Utilities staff provide program
management oversight and leads field sampling activities of this program. Annual and 5-year water quality reports
as well as seasonal updates are made available to the public via the Utilities website. (Attachment 6)
Horsetooth Reservoir Water Quality Monitoring
The Water Utility maintains a 20+ year record of water quality in Horsetooth Reservoir. Beginning in 2015, the
Utility moved from an in-house monitoring program to a cost-shared monitoring program with Northern Water.
This partnership reduced redundancies in effort and offers significant cost-savings for the Water Utility. Under this
agreement, Northern Water collects samples from Horsetooth Reservoir as part of their baseline water quality
monitoring program and the City provides approximately $4000 each year through in-kind contribution of water
quality analyses. Northern Water also provides the City all Horsetooth Reservoir water quality data and related
reports.
Big Thompson Watershed Forum (BTWF)
The BTWF manages a water quality monitoring program on the Big Thompson River at key locations that
influence water quality in Horsetooth Reservoir, as well as other locations on the Big Thompson River that are of
interest to the funding partners. The City of Fort Collins, along with the Cities of Loveland and Greeley, and
Northern Water are major funders for the BTWF and retains a seat on the BTWF Board of Directors. The Soldier
Canyon Water Treatment Authority also contributes. The BTWF holds a joint-funding agreement with the USGS
for the collection of all water quality sampling activities. Annual water quality reporting activities are managed by
BTWF staff.
Poudre River Monitoring Alliance (PRMA)
The PRMA is a group of seven wastewater dischargers on the Poudre River who coordinate efforts to assist
participants in meeting sampling requirements of certain water quality regulations and to demonstrate stewardship
by tracking the quality of the Poudre River over time. The geographical scope of this program spans from just
above the City’s Mulberry Water Reclamation Facility to downstream of the City of Greeley’s outfall near the
confluence with the South Platte River. Utilities Watershed Program staff manage the PRMA while the Utilities
Pollution Control Laboratory staff conduct the water quality sampling for the City and conduct sample analysis and
reporting for the program partners. The Water Utility funds approximately $24,000 for maintenance of five PRMA
sampling sites, with approximately 67% of the total cost offset by in-kind contributions of laboratory services.
Halligan Water Supply Project
Water quality studies are critical for the Project’s ongoing federal permitting and the required State water quality
certification process. Currently, Watershed Program staff are collecting water quality information on Halligan
Reservoir as well as the North Fork of the Poudre River. The data has been and will continue to be used to
construct detailed water quality models, which will be used for future river health work.
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State of the Poudre-A River Health Framework and Report Card
A collaborative project between Natural Areas and Utilities, the River Health Assessment Framework (RHAF) is a
tool to understand current and future stresses on the Poudre River from the lower Poudre Canyon to just below I-
25 and align management practices with desired outcomes. The RHAF is built around 10 indicators that represent
the essential physical, chemical, and biological elements of the river ecosystem, The tool uses an academic
grading scale (A, B, C, D, and F) to relate the sense of health or impairment in a way that is designed to be easily
understandable. Grading guidelines provide specific criteria to describe the existing condition and/or magnitude of
dysfunction to warrant a given grade. Each indicator and its metrics can be quantitatively evaluated, but lacking
specific data, metrics can be assessed using best professional judgement following the established grading
guidelines. The findings and grading for each zone of the River are summarized in the Poudre River Health
Report Card. (Attachment 7)
The RHAF is significant because it supports the broad set of watershed services that a healthy River provides to
the City. These include a reliable water supply; floodplain and stormwater management; clean water; ecological
health; and a source of recreation, health and wellness for the community. There are a diverse and complex set
of City objectives related to these watershed services and the RHAF, through data and metrics provides insight
into how the City can improve outcomes for the community.
Key Partnerships
As noted above, the Poudre River provides a broad set of watershed services to a diverse set of stakeholders,
including the City. Collaboration is critical to ensuring that this shared resource is healthy and resilient. To that
end, the City has and will continue to engage in many partnerships to support the City’s goal of sustaining a
healthy and resilient river. Some of these partnerships are highlighted in sections above. Additional partnerships
of note include:
Water Supply Partnerships
The Water Utility collaborates with other water users of both the Poudre River and Horsetooth Reservoir through
water sharing agreements, water sales and delivery agreements, shared infrastructure, and other specific
agreements. For example:
x In 2013, FCLWD purchased 5 million gallons of excess capacity in the Water Utility’s Water Treatment
Facility.
x The Water Utility and the Soldier Canyon Treatment Authority partnered in 2013 to fund the pre-sedimentation
basin on the Pleasant Valley Pipeline to pretreat runoff from the High Park Fire.
x The Water Utility’s Water Treatment Facility and Soldier Canyon Filter Plant utilize interconnects between the
two water systems to share water during plant shutdowns and in other scenarios where additional treated
water is needed by either party.
x City staff partnered with ELCO and FCLWD in 2018 to host a Growing Water Smart Workshop focused on the
nexus between water and land use planning. This effort served as a foundation for future water resource
planning in the Growth Management Area and integration of that planning into the recent City Plan update.
Regional Water Projects
In addition to the City’s Halligan Water Supply Project (Halligan), there are five other major water supply projects
in the Northern Colorado region. They include the Northern Integrated Supply Project (NISP), the Seaman Water
Supply Project (Seaman), the Thornton Water Project (Thornton), the Windy Gap Firming Project and the Moffat
Collection System Project. These projects are in various stages of permitting. Utilities and other City staff have
focused mainly on the projects that effect the Poudre River, which include the Halligan, NISP, Thornton, and the
Seaman.
Northern Integrated Supply Project (NISP)
The Northern Integrated Supply Project (NISP) is a water development and storage project proposed by the
Northern Water on behalf of 15 municipalities and water providers, mainly south and east of Fort Collins. FCLWD,
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which serves portions of southeast Fort Collins, is a NISP participant and will receive water from the project.
NISP will draw water from the Poudre River. One of two proposed reservoirs for NISP, “Glade Reservoir” will be
located near Ted’s place north of Fort Collins. In order to be constructed, NISP needs a variety of permits and
approvals from federal, state, and local entities.
City Staff has been actively involved in NISP and NISP-related issues since the federal permitting process began
in 2004. The City has submitted official comments prepared on various NISP permitting documents, such as: the
draft environmental impact statement (“EIS”) in 2008; the supplemental draft EIS in 2015; the fish and wildlife
mitigation and enhancement plan in 2017; and the final EIS in 2018. In addition to official comments, City Council
authorized and directed City Staff in Resolution 2018-053 “to meet with Northern Water to seek to negotiate
regarding NISP, and if Northern Water is so willing, to engage in negotiations regarding NISP.”
Pursuant to that direction, City Staff and Northern Water (on behalf of the NISP participants) have met 8 times
(between August 2018 and May 2019) to discuss the key priorities for both the City and Northern Water. The
priorities that have been discussed are those described in Resolution 2018-053 and include:
x Water quality;
x Maintaining resilience and mitigating flood risk;
x Adequate availability of water supply to serve the region;
x Leveraging shared resources;
x Maintaining and enhancing the health of the Poudre River corridor, including environmental flows; and,
x Development of a structured and effective adaptive management approach.
Discussions to date have also included identification of options for addressing these priorities with a focus on
options that are mutually beneficial to both parties. Some examples of opportunities discussed to date include:
x Partnering on flood risk and stormwater quality mitigation in areas of the Poudre River Corridor that are high
priorities for both the City and for the NISP participants;
x Exploration of various management approaches for maintaining cooler temperatures in the Poudre River,
particularly from Lemay Avenue to I-25;
x Exploration of options for the City to facilitate the NISP low flow conveyance realignment (i.e. diverting NISP
water further downstream than initially planned for NISP) in support of maintaining minimum flows in the river
through town as far downstream as feasible;
x Exploration of options to maintain springtime peak flows in the river, including the potential use of City water
rights to create an environmental pool in Glade Reservoir;
x Collaboration on a study to identify sources of E. coli contamination in stormwater runoff; and,
x Partnering on retrofits of existing river diversion structures to facilitate fish and flow passage and support river
connectivity.
The adaptive management approach outlined in NISP’s plans and environmental impact statement, and an
overall collaborative framework to support a healthy Poudre River is a significant topic of focus in these
discussions. Components of this conversation include:
x Adaptive management/collaborative framework governance structure;
x Identification of NISP’s predicted impacts and associated adaptive management and mitigation commitments,
and ecological objectives and how those commitments intersect with an overall healthy Poudre River strategy;
x The role of the City in NISP’s adaptive management program;
x The level of funding needed from NISP to support their adaptive management commitments; and,
x Opportunities to utilize consistent data collection, analysis, and reporting methodology to support both the
NISP adaptive management approach and the overall Poudre River collaborative framework.
City Staff will continue to meet with Northern Water to develop approaches and potential agreements or other
instruments to memorialize commitments related to the priorities outlined above. Any draft agreements between
the City and Northern Water would require approval by the City Manager or City Council pursuant to City Code
Section 1-22.
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Natural Areas River Partnerships
As part of their core mission, the City’s Natural Areas Department (NAD) purchases properties in the Poudre
River floodplain for the purpose of conserving habitats. Because floodplain habitats are dependent on conditions
in the river, NAD takes a multi-pronged approach to supporting Poudre River health. To accomplish the whole
river system health objective and support other City initiatives, NAD engages with staff in the Water Utility,
Wastewater Utility, Stormwater Utility, Parks, and Parks Planning to ensure an integrated approach and to enable
a project to meet multiple objectives.
The NAD program has been working on restoring the river-floodplain connection to foster both aquatic and forest
health. Because there are many diversion structures on the Poudre River, fish populations are prevented from
accessing upstream and downstream habitats they need to thrive. NAD has been working with key partners to
install fish passage to allow fish to move upstream as needed.
The Water Utility and Natural Areas also partnered on the construction and operation of Rigden Reservoir.
Partnering allowed reduced costs for construction to both entities and helped Natural Areas improve adjacent
properties including Topminnow and Running Deer Natural Areas.
Instream Flow Augmentation Plan
Natural Areas engages in a variety of regional water and flow related initiatives to protect or improve flow in the
river. High spring flows are central to maintaining healthy habitats and during the fall and winter months the
Poudre River experiences extremely low flows in certain places. Consequently, NAD and other City Staff are
working to maintain the critical high flows as well as developing mechanisms for improving low flows. One such
effort is being part of a regional collaborative to establish a legal mechanism for local water users to add water to
the Poudre River and to protect that additional water from being diverted by others while it is in the river. This
effort was previously known as an “instream flow augmentation plan,” but is now more commonly called the
“Poudre Flows Plan” (the “Plan”).
Since 2013, the City has worked collaboratively with other Poudre River stakeholders (including the City of
Thornton, the City of Greeley, Northern Water, the Cache a Poudre Water Users Association, the Colorado Water
Conservation Board, and Colorado Parks and Wildlife) to develop the Plan with the goal of augmenting flow in the
river for environmental benefit. If successful, the Plan could present a new approach for the development and
protection of instream flows below the canyon mouth of the Poudre River, which is an objective that has been
discussed for at least 40 years and that at times has appeared virtually unattainable. The Plan is an innovative
application of Colorado water and remains in development.
CONCLUSION
The Water Utility is focused on providing high quality, reliable water service to our customers in an efficient
manner. We utilize many strategies to meet our service commitments and continually seek to improve the level of
service we provide. Key strategies related to water supply and water quality may be summarized as follows:
1. Planning – we plan so that we may provide reliable, high-quality water service to current and future
customers.
2. Monitoring – we monitor the quality of our source water and our finished water to protect public health and
to provide treated water of the highest quality.
3. Watershed Resiliency – we invest resources in protecting our watershed and natural resources so that we
may be resilient to a changing climate and other vulnerabilities.
4. River Flows – we seek opportunities to promote both high flows and maintenance of low flows to support
river health.
5. System Renewal – we are proactive in renewing our system as to eliminate and or minimize service
interruptions and to contribute to the safety of our community.
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6. Partnerships – we are committed to collaborating with key partners to ensure we utilize our water
resources in an efficient and effective manner while protecting river health and its ecosystem.
These strategies support our water supply, watershed, and water quality programs to ensure the level of water
service that our community deserves.
ATTACHMENTS
1. Water Districts Map (PDF)
2. Water Supply System Map (PDF)
3. Halligan Water Supply Project Agenda Item Summary (PDF)
4. 2012 Water Supply and Demand Management Policy (PDF)
5. Fort Collins Source Watersheds Map (PDF)
6. 2017 Five Year Upper Poudre River Water Quality Report (PDF)
7. Poudre River Health Report Card (PDF)
8. PowerPoint Presentation (PDF)
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1
City of Fort Collins
Water Supply and Demand Management Policy
The City of Fort Collins’ Water Supply and Demand Management Policy provides a
foundational framework for water supply and demand management decisions concerning the
City’s water supply system. Operational and management actions and decisions by the Water
Utility will be consistent with the provisions of this policy.
Objective
To provide a sustainable and integrated approach to 1) ensuring an adequate, safe and reliable
supply of water for the beneficial use by customers and the community and 2) managing the level
of demand and the efficient use of a scarce and valuable resource consistent with the preferences
of Water Utility customers and in recognition of the region’s semi-arid climate.
This objective aligns with the 2010 Plan Fort Collins that provides a comprehensive 25-year
vision for the future development of Fort Collins. Policy ENV 21.2 of Plan Fort Collins states,
“Abide by Water Supply and Demand Management Policy: Provide for an integrated approach to
providing a reliable water supply to meet the beneficial needs of customers and the community
while promoting the efficient and wise use of water.”
This Water Supply and Demand Management Policy calls for a “sustainable and integrated
approach” to water demand and water resources management. Sustainability is defined within
the context of the triple-bottom-line decision making in Plan Fort Collins as, “To systematically,
creatively, and thoughtfully utilize environmental, human, and economic resources to meet our
present needs and those of future generations without compromising the ecosystems upon which
we depend.” Aligning with Plan Fort Collins, the Water Utility will take a leadership role by
incorporating the triple-bottom-line in its management of water supply and demand. When this
core value is applied to the use and development of our valuable water resources, the Utility will
strive to:
Avoid, minimize or offset impacts to our environment
Consider the social benefits of having a reliable and high quality water supply for health and
safety, economic prosperity and healthy landscapes, as well as a healthy natural environment
Analyze the cost to provide such supplies, while also considering the effects it has to our
local and regional economies
Managing water supply and demand is a dynamic process that evolves along with changes in
data management and technology, legal and political environments, economic development and
water innovation, and as the State’s population continues to increase. Given these factors, it is
important to maintain an up-to-date effective policy that is based on current data. The policy’s
terms and conditions should be reviewed and updated by 2020, or sooner if desired by the City
Council or the Utilities Executive Director.
ATTACHMENT 4 2.4
Packet Pg. 71
Attachment: 2012 Water Supply and Demand Management Policy (8063 : Water Resources, Watershed, and Water Quality Protection Overview)
2
1.0 WATER USE EFFICIENCY AND DEMAND MANAGEMENT
The City views its water use efficiency program as an important proactive response to supply
variability and climate change. Elements of the City’s conservation program include reducing
indoor demand through improved technology, leak reduction and behavior change and reducing
outdoor demand through improved irrigation efficiency and reasonable changes in landscaping.
The City believes water use efficiency is of vital importance for many reasons, including to:
Foster a conservation ethic and eliminate waste
Demonstrate a commitment to sustainability
Provide water for multiple beneficial purposes
Reduce the need for capital expansion projects and certain operational costs
Prepare for potential impacts of climate change
1.1 Water Use Efficiency Goals for Treated Water Use
The City’s 2009 Water Conservation Plan1 established a goal of reducing the City’s treated water
use to 140 gallons per capita per day (gpcd)2 by the year 20203. The City will utilize water use
efficiency measures and programs with the aim of reducing its water use to an average of 140
gpcd, subject to 1) continuing study of the water requirements of the City’s urban landscaping, 2)
impacts on water demand due to changes in land use policies, building codes and housing trends,
3) additional studies on climate change, and 4) changes in the water use goal as may be adjusted
by any subsequent water conservation plans. This water use goal is subject to change as
discussed above and is intended as a goal that can be met while sustaining reasonable indoor and
outdoor values of the City.
The per capita peak daily demand4 will be reduced or maintained to be no more than 350 gpcd by
the year 2020, but may be adjusted by any subsequent water conservation plans.
1.2 Water Use Efficiency Program
Policy ENV 21.2 of Plan Fort Collins states, “Conservation measures should be implemented in
accordance with the Water Conservation Plan and periodically adjusted to reflect new and
effective conservation measures.” The City will optimize water use efficiency through the
programs and measures specified in its Water Conservation Plan. These programs and measures
include educational programs, incentive programs, regulatory measures and operational
measures. Specific measures and programs are outlined in the Water Conservation Plan.
1 State guidelines are changing the terminology of Water Conservation Plans to Water Use Efficiency Plans, and
likewise conservation is being changed to water use efficiency. For purposes of this policy, water use efficiency is
referred to as water conservation; however, the terminology may be used interchangeably.
2 Gallon per capita per day (gpcd) calculations are based on the total treated water produced at the Water Treatment
Facility for use by Water Utility customers (minus large contractual customers and other sales or exchange
arrangements) divided by the estimated population of the Water Utility’s service area.
3 This goal represents an 8.5% reduction in water use compared to Fort Collins’ 2006-2010 average daily water use
of 153 gpcd. It represents a 29% reduction in water use compared to Fort Collins’ pre-drought (1992-2001) average
daily water use of 197 gpcd.
4 The peak daily demand is 2.5 times the average daily use water conservation goal and is based on historic ratios of
average to peak daily use.
2.4
Packet Pg. 72
Attachment: 2012 Water Supply and Demand Management Policy (8063 : Water Resources, Watershed, and Water Quality Protection Overview)
3
The overall effectiveness of these measures and programs will be evaluated on a regular basis
and if necessary, modifications will be made to increase effectiveness or to modify the City’s
water use goal. An annual water conservation report will be prepared to describe the status and
results of the various measures and programs. The Water Conservation Plan will be updated at a
minimum of every seven years, as currently required by the State of Colorado.
1.3 Water Rate Structures
The City will have stable water rate structures with transparent accountability for all classes of
customers. The water rate structures will provide an economic incentive to use water efficiently
while also providing sufficient revenue for operational and maintenance purposes. Examples of
structures that may be utilized include 1) tiered rates with increasing prices as water use
increases, 2) seasonal blocks with higher rates during the irrigation season, and 3) water budget
approaches based on appropriate targets for individual customers.
The City will annually review the effectiveness of its water rate structures as part of its financial
analyses regarding Water Utility revenue, expenses and rates. Specific studies or changes to the
rate structure may be made upon identification of the need to revise it. Any changes to the rate
structure will require City Council approval.
1.4 Population Growth
Population growth is an important factor in determining the City’s water supply needs, since
increases in population generally increase the need for additional supplies. Population growth
projections and associated water demand are mostly a function of land use planning,
development densities, annexation and other growth related issues that can be affected by City
Council decisions. The Water Utility will continue to work closely with the Current Planning
Department, which provides population projections that may be effected by changes in City
policies related to growth.
2.0 WATER SUPPLY RELIABILITY
The City needs to meet future water demands in an efficient and reliable manner. Policy ENV
21.2 of Plan Fort Collins states, “Water supply reliability criteria will take into consideration
potential effects of climate change and other vulnerabilities. Water supplies and related facilities
shall be acquired or developed after careful consideration of social, economic and environmental
factors.” One of the Water Utility’s primary objectives is to provide an adequate and reliable
supply of water to its customers and other water users. Key principles that need to be considered
when addressing water supply for municipal use include:
Providing water supply system reliability and flexibility
Considering a broad portfolio of resources that do not overly depend on any one source
Maintaining a water storage reserve for unforeseen circumstances
Maintaining water supply infrastructure and system security
Being a steward of the City’s water resources, which includes watershed management
Collaboration with the City’s regional water providers and users
Maintaining awareness of state, national and worldwide trends and adapting as needed to
meet our customer needs
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2.1 Water Supply Planning Criteria
An integral component of the City’s water supply planning efforts is to maintain computer
models that estimate the yield of its existing and future water supplies. The following water
supply planning criteria are key parameters used in these models that provide a foundation for
planning future supplies.
2.1.1 Planning Demand Level
The reliability of the City’s water supply should be maintained to meet an average per capita
demand level of 150 gpcd5,6. This planning level provides a value that is higher than the water
use goal to address uncertainties inherent in water supply planning.
It is important to have a planning number that can be used for development of long-range water
supply facilities. Because water supply system infrastructure may take many years to permit and
construct, it is desirable to use conservative assumptions to size facilities that may be needed for
the long-term. A planning demand level should be larger than the water use goal, primarily
because of the uncertainties related to projected water demands, yields from specific water
rights, climate change and other unanticipated effects.
2.1.2 Drought Criterion
The reliability and capacity of the City’s water supply system should be maintained to meet the
planning level demand during at least a l-in-50 year drought event in the Cache la Poudre River
Basin. Water rights should be acquired and facilities (including storage capacity) should be
planned and constructed sufficiently ahead of the time to maintain the 1-in-50 year drought
criterion, considering the time required to obtain water court decrees and permit and construct
diversion, conveyance and/or storage facilities. In using this criterion, the City seeks to provide a
balance among water supply reliability, the financial investment necessary to secure such
reliability and the environmental impacts associated with water storage and diversions.
2.1.3 Storage Reserve Factor
The City’s water supply planning criteria will include a storage reserve factor that equates to
20% of annual demand in storage through a 1-in-50 year drought7,8. This factor provides an
additional layer of protection intended to address dimensions of risk outside of the other
5 The 150 gpcd value is based upon the normalized 2006-2011 average daily use.
6 The average per capita demand planning level is used for facility planning purposes. Gallons per capita per day
(gpcd) calculations are based on the total treated water produced at the Water Treatment Facility for use by Water
Utility customers (minus large contractual customers and other sales or exchange arrangements) divided by the
estimated population of the Water Utility’s service area. This number is multiplied by population projections
developed by the City’s Planning Department to calculate future water demands.
7 For the Water Utility, 20% of annual demand is equivalent to around 3.7 months of average winter demand and
about 1.5 months of average July demand.
8 In meeting this factor, it is assumed that the City cannot rely on the existing Colorado-Big Thompson Project
(CBT) carryover program. This program currently allows each CBT unit holder to carry over up to 20% of its CBT
unit ownership in CBT reservoirs for use in the following year. However, this program has varied over the years and
there is no guarantee that it will be continued in the future.
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reliability criteria, including emergency situations (i.e. pipeline failure) and droughts that exceed
a 1-in-50 year drought.
2.2 Climate Change
Climate change could significantly impact the reliability of the City’s supplies and/or the amount
of water required to maintain existing landscapes9; however, there is a great deal of uncertainty
related to current climate change projections along the Colorado Front Range and its impact on
municipal demands and water supply systems. The City’s planning criteria and assumptions are
conservative in part to account for climate change based on the information to date. The City will
continue to monitor climate change information and, if necessary, will revise its water supply
planning criteria and assumptions to ensure future water supply reliability.
2.3 Water Supply Shortage Response Plan
The City will maintain a plan for responding to situations where there are projected water supply
shortages, either because of severe drought conditions (i.e., greater than a 1-in-50 year drought)
or because of disruptions in the raw water delivery system. When needed, the Water Supply
Shortage Response Plan will be activated based on the projected water supply shortage.
This plan will include measures to temporarily reduce water use through media campaigns,
regulations, restrictions, rate adjustments and other measures. The plan may also include
provisions to temporarily supplement the supply through interruptible water supply contracts,
leases, exchanges and operational measures. Reducing the City’s water use during supply short
situations may lessen adverse impacts to irrigated agriculture and flows in the Poudre River. The
plan will be reviewed periodically and, if necessary, updated to reflect changes in the City’s
water use and its water supply system.
2.4 Additional Supplies and Facilities
In order to meet projected growth within the Water Utility’s service area, as well as maintain
system reliability and operational flexibility, the City will need to increase the firm yield of its
current water supply system. The following policy elements address ways of meeting these
needs.
2.4.1 Raw Water Requirements for New Development
The City shall require developers to turn over water rights as approved by the City, or cash in-
lieu-of water rights, such that supplies can be made available to meet or exceed the demands of
the Water Utility’s treated water customers during a l-in-50 year drought.
Cash collected shall be used to increase the firm yield and long-term reliability of the City’s
supply system. Potential uses of cash include acquiring additional water rights, entering into
9 Current research indicates that changes in precipitation in this area are uncertain but that temperatures will increase
and therefore it is likely that runoff will come earlier and in a shorter amount of time, precipitation may more often
come as rain, and higher temperatures will increase outdoor demands and change growing seasons for existing
landscapes.
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water sharing arrangements with agricultural entities, purchasing or developing storage facilities
and pursuing other actions toward developing a reliable water supply system. Consideration will
be given to providing a diversified system that can withstand the annual variability inherent in
both water demands and supplies. The balance between water rights being turned over and cash
received by developers should be monitored and adjusted as needed to develop a reliable and
effective system.
2.4.2 Acquisition and/or Sharing of Agricultural Water Supplies
The City currently owns and will acquire additional water rights that are decreed only for
agricultural use. The City will periodically need to change these water rights from agricultural
use to municipal use to meet its water supply needs. The City will change those rights that come
from areas upon which the City is growing, or from areas where the irrigation has ceased, when
needed. For water rights that were derived from irrigated agricultural lands that remain in viable
agricultural areas, the City will refrain from converting agricultural decrees to municipal use as
long as other water supply options are available or other factors make it prudent to do so. The
City will also work towards water sharing arrangements that provide water for municipal uses
when critically needed and that allow for continued agricultural use of water at other times, in a
manner that preserves irrigated agricultural lands over the long-term.
2.4.3 Facilities
The City will pursue the acquisition or development of facilities that are needed to manage the
City’s water rights in an efficient and effective manner and enhance the City’s ability to meet
demands through at least a 1-in-50 year drought. These facilities may include storage capacity,
diversion structures, pipelines or other conveyances, pumping equipment, or other facilities that
increase the firm yield of the City’s supply system.
Additional storage will be acquired or constructed considering 1) the City’s return flow
obligations incurred from changes of water rights, 2) the City’s need to carryover water from wet
years to dry years in order to meet its drought criteria, 3) operational flexibility, redundancy and
reliability of the City’s water supply system, and 4) potential multiple-use benefits (i.e.,
environmental flows, recreational uses, etc.). The City will analyze the potential environmental
impacts of developing storage along with other associated costs and benefits, and will develop
that storage in a manner that avoids, minimizes or offsets the effects to the environment. Storage
capacity options include the enlargement of Halligan Reservoir, the development of local gravel
pits into storage ponds, the acquisition of storage capacity in new or existing reservoirs, the
development of aquifer storage, or some combination of the above.
3.0 TREATED AND RAW WATER QUALITY
Policy ENV 21.1 of Plan Fort Collins states, “Develop and adhere to drinking water quality
standards, treatment practices, and procedures that provide the highest level of health protection
that can be realistically achieved.” In addition, the City will take an active role in protecting the
quality of water in the various watersheds from which the City’s raw water is derived and
maintaining the taste and quality of the City’s treated water. This may include mixing of the
City’s source waters to maintain high water quality and require collaboration with private,
county, state and federal land owners and managers. The acquisition, development, and
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management of the City’s raw and treated water will be consistent with the City’s Drinking
Water Quality Policy and other applicable policies related to watershed protection and water
treatment.
4.0 USE OF SURPLUS RAW WATER
The City will use its existing supplies to meet municipal obligations with the following priorities:
1) to meet water demands by the City’s treated water customers, and 2) to meet the City’s raw
water needs as well as other City raw water obligations. Raw water needs include use for such
purposes as irrigation of City parks, golf courses, cemeteries and other greenbelt areas.
Additional raw water obligations include primarily water transfers to other entities because of
agreements or exchanges made to manage the water supply system more effectively.
Water not needed for the above purposes is referred to as surplus water and may be made
available to others in accordance with decrees and other applicable policies. Since the City plans
its water supply system using a 1-in-50 year drought criterion, it typically has significant
quantities of surplus raw water in many years. This surplus water may be available on a year-to-
year basis or through multi-year arrangements that do not significantly impair the City’s ability
to meet municipal demands. The City will continue to rent its surplus supplies at a fair market
price that helps offset the cost of owning such supplies and benefits the Water Utility ratepayers.
4.1 Commitment to Other Beneficial Purposes
Acknowledging that the City’s use of its valuable water resources has impacts to the
environment and the region, the City will commit to using its surplus supplies for other
beneficial purposes such as supporting irrigated agriculture, supplementing flows in the Poudre
River or providing other regional benefits. The City’s surplus supplies come from a variety of
sources, each of which has unique characteristics. These sources include CBT water and shares
in several irrigation companies. Some sources are more suitable and available than others to meet
beneficial purposes. Whether the surplus raw water can be used for these other purposes is
dependent upon a number of factors, including the type of water, place of use and other decree
limitations. Any potential use of these supplies should consider, and will likely require
coordination with, other water users, state agencies and other groups. Some uses of the surplus
supplies, such as maintaining an instream flow according to the State’s Instream Flow Program,
may require a change of water rights through the water court process. The City will engage in a
thorough evaluation of these issues as part of assessing the use of its surplus supplies for these
beneficial purposes.
Utilities will evaluate implementing a program to allow voluntary contributions from its
ratepayers (i.e., Utility bill “check-off box”) for programs that are designed to support the
following purposes: preserving local agriculture, supplementing flows in the Poudre River, or
meeting other beneficial purposes that our community may desire.
4.1.1 Agriculture and Open Space
Policy SW 3.2 of Plan Fort Collins states, “Participate in and follow the Northern Colorado
Regional Food System Assessment project and other Larimer County agricultural efforts, and
implement their recommendations at a local level, if appropriate.” In addition, Policy LIV 44.1
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of Plan Fort Collins states, “Maintain a system of publicly-owned open lands to protect the
integrity of wildlife habitat and conservation sites, protect corridors between natural areas,
conserve outstanding examples of Fort Collins' diverse natural heritage, and provide a broad
range of opportunities for educational, interpretive, and recreational programs to meet
community needs.” To the extent that surplus water is available, the City will continue to support
the local agricultural economy and help preserve the associated open spaces by renting surplus
agricultural water back to irrigators under the respective irrigation companies.
The City will explore long-term rental and sharing arrangements with irrigators10 in order to
support the regional food system, encourage agricultural open space and other benefits provided
by irrigated agriculture, as well as benefit the Water Utility ratepayers.
4.1.2 Instream Flows
Policy ENV 24.5 of Plan Fort Collins states, “Work to quantify and provide adequate instream
flows to maintain the ecological functionality, and recreational and scenic values of the Cache la
Poudre River through Fort Collins.” Recognizing that its water use depletes natural streamflows,
the City will seek opportunities to improve, beyond any associated minimum regulatory
requirements, the ecological function of the streams and rivers affected by its diversions. The
Water Utility will take a leadership role in working with other City departments, local and
regional groups and agencies towards the following objectives in accordance with Colorado
water law and the administration of water rights in Colorado: 1) encourage flows in local streams
to protect the ecosystem, 2) pursue the operation of its water supplies and facilities in a manner
that avoids, minimizes or offsets the effects to the environment while meeting customer
demands, and 3) explore projects or measures that would provide flows in streams and water in
reservoirs for recreational and aesthetic purposes.
4.1.3 Other Arrangements
The City will consider and participate in other surplus water supply arrangements with other
entities that provide mutual benefits and support the region. These may include other rental
agreements, augmentation plans and other cooperative arrangements with regional partners.
These types of arrangements should be limited to unique opportunities that are mutually
beneficial to the parties and provide significant social, economic or environmental benefits to the
region.
5.0 REGIONAL COOPERATION
The City recognizes the importance in maintaining good relationships with regional entities and
coordinating efforts to achieve mutual goals. The City also recognizes that growing Colorado
municipalities are currently struggling to define a way to meet future water supply needs in a
manner that minimizes negative impacts to agricultural economies and river ecosystems. The
Water Utility will endeavor to be a leader in demonstrating how water supply can be provided in
a manner that respects other interests.
10 The City’s largest irrigation company ownership interest is in the North Poudre Irrigation Company, which still
has substantial lands in irrigated agricultural production and has a unique mix of native water and CBT water that
lends itself to these types of partnership arrangements.
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5.1 Working with Other Municipal Providers
The City will continue to work with the water suppliers throughout the northern Colorado Front
Range to assure that adequate supplies are maintained in the region. When benefits are identified,
the City will cooperate with area entities in studying, building, sharing capacity and operating
water transmission lines, distribution systems and storage reservoirs for greater mutual benefit.
The City has common interests and the potential to cooperate with regional entities including the
water districts around Fort Collins, the City of Greeley and the Northern Colorado Water
Conservancy District, as well as other Colorado water providers. In particular, the City should
work closely with water districts that serve Fort Collins residents to encourage similar policies
regarding drought protection, conservation and to provide mutual assistance during emergencies.
5.2 Working with Local Irrigation Companies
The City will continue to cooperate with local irrigation companies regarding the use, exchange
and transfer of water in the Cache la Poudre River Basin. As a major shareholder in many of the
local irrigation companies, it is necessary and desirable that the City work closely with these
companies. Much of the water supply available to the City is through the ownership of shares in
local irrigation companies.
5.3 Working with Others
City Departments will work together and also cooperate with local, state and federal agencies,
civic organizations, environmental groups and other non-governmental organizations when
common goals would benefit City residents and the surrounding community. Examples of goals
that may involve City water supplies and be worthy of collaborative efforts include support for
existing and development of new local food sources, promoting open space, improving river
flows and supporting the local economy. Such efforts should identify appropriate entities and
sources of revenue for specific goals or projects.
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Map showing the locations of the City of Fort Collins’ source watersheds
Horsetooth Reservoir Outlet
Poudre River Intake
FC Water Treatment Facility
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WATER QUALITY
TRENDS REPORT
2008 – 2017
Upper
Cache la Poudre
Watershed
Collaborative
Water Quality
Monitoring Program
June 25, 2018
PREPARED FOR:
Fort Collins Utilities
City of Greeley
Soldier Canyon Water Authority
PREPARED BY:
Jared Heath, Watershed Specialist
Richard Thorp, Watershed Program Manager
Leslie Hill, Quality Assurance Coordinator
City of Fort Collins Utilities
Water Quality Services Division
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EXECUTIVE
SUMMARY
BACKGROUND
The Upper Cache la Poudre Collaborative Water Quality
Monitoring Program (hereafter referred to as the Upper
CLP monitoring program) is designed to assist the City of
Fort Collins, the City of Greeley and the Soldier Canyon
Water Treatment Authority (formerly Tri-Districts) in
meeting current and future drinking water treatment goals
by reporting current water quality conditions and trends
within the Upper Cache La Poudre River (CLP) watershed
and summarizing issues that potentially impact watershed
health. Annual reports were published in 2008 through
2011 and 2013 through 2016. The last five-year report was
published in 2012.
SCOPE OF THE 2017 WATER QUALITY
TRENDS REPORT
This water quality trends report analyzes the hydrology,
climate, and water quality in the Upper CLP watershed over
the last decade. Water quality data collected throughout
the Upper CLP watershed were analyzed for long-term
trends to determine if concentrations increased, decreased
or stayed the same over the ten-year period of record from
2008 to 2017. This report documents 1) watershed impacts
and issues of concern; 2) significant trends in climate,
hydrology, and water quality in the Upper CLP watershed;
3) potential sources of pollution and/or watershed
disturbances influencing water quality trends; and 4) a
summary of significant findings and implications to water
treatment.
STATE OF UPPER CACHE LA POUDRE
WATERSHED
Watershed Impacts & Issues of Concern
Over the past ten years the Upper CLP watershed has
experienced periods of wet and dry water years influencing
both streamflow and water quality conditions in the CLP
watershed. Exceptionally hot and dry conditions in 2012 led
to extreme drought and two major wildfires in the
watershed. In the following year, a long-duration, high
intensity rainfall event brought severe flooding in streams
and rivers throughout the Upper CLP watershed. These
two events signify the extreme variability in the hydrology,
and weather of the Upper CLP watershed and highlight
potential future climate driven events that may impact water
quality.
Forest insects and diseases have impacted the Upper CLP
watershed over the past two decades. Although, recent
surveys show the mountain pine beetle epidemic is
declining, expanding outbreaks in Engelmann spruce
forests suggests that forested watershed continue to be
susceptible to forest insects and disease.
Watershed impacts caused by climate change and
atmospheric deposition are less clear, but remain a major
threat to future watershed processes and water quality.
Unlike extreme-weather driven disturbances, the
watershed response from climate change and atmospheric
deposition impacts may be subtle emphasizing the
importance of continued monitoring through the Upper CLP
watershed.
iv UPPER CACHE LA POUDRE WATERSHED COLLABORATIVE WATER QUALITY MONITORING PROGRAM
Trends were detected at varying scales. Both site-specific
and watershed-wide trends were detected in the Upper
CLP watershed. Site-specific trends capture impacts to a
specific site, while watershed-wide trends imply a large
disturbance that impacted the entire basin or large areas of
basin impacting multiple monitoring locations.
Implications to Water Treatment
Long-term trends in certain water quality parameters may
pose issues to water treatment processes in the future. It
is anticipated that water quality impacts caused by recent
wildfire and flooding will recover with time. Wildfire
impacted water quality parameters are trending toward
baseline conditions in recent years implying watershed
recovery. However, climate change projections for
Colorado point to a warmer climate and unpredictable
precipitation patterns that will likely increase the frequency
and severity of drought and wildfires, and other extreme-
weather events that can impact water quality.
Water quality changes were detected for the following
parameters near the City of Fort Collins’, City of Greeley’s
and Soldier Canyon Water Authority’s raw water intakes:
x Alkalinity and hardness
x pH
x Total dissolved solids
x Total organic carbon
x Nutrients
x Total coliforms
In general, the water treatment facilities should continue to
closely monitor key water quality parameters and may be
required to adjust blending ratios and chemical additions to
meet current water treatment goals. Routine water quality
monitoring throughout the Upper CLP watershed will allow
the Upper CLP Collaborative Monitoring Program to
continue to sustain a long-term data record providing
program partners with valuable information on short and
long-term trends that may arise in the future.
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TABLE OF CONTENTS
EXECUTIVE SUMMARY.............................................................................................................................................................III
Background.............................................................................................................................................................................
iii
Scope of The 2017 Water Quality Trends Report................................................................................................................... iii
State of Upper Cache la Poudre Watershed........................................................................................................................... iii
TABLE OF FIGURES................................................................................................................................................................ VII
LIST OF TABLES.......................................................................................................................................................................
IX
LIST OF ABBREVIATIONS & ACRONYMS............................................................................................................................... XI
1.0 INTRODUCTION....................................................................................................................................................................1
1.1 Background.................................................................................................................................................................1
1.2 Watershed Description and Sampling Locations ........................................................................................................1
1.3 Sampling Plan and Parameters..................................................................................................................................1
1.4 Sample Collection and Analysis .................................................................................................................................2
1.5 Scope of Five Year Report .........................................................................................................................................3
2.0 WATERSHED IMPACTS & ISSUES OF CONCERN.............................................................................................................5
2.1 Climate Change..........................................................................................................................................................5
2.2 Drought and Wildfire...................................................................................................................................................5
2.3 Flooding......................................................................................................................................................................6
2.4 Forest Insects and Disease ........................................................................................................................................7
2.5 Air Pollution.................................................................................................................................................................7
3.0 WATERSHED HYDROLOGY AND CLIMATE .......................................................................................................................9
3.1 Air Temperature..........................................................................................................................................................9
3.2 Precipitation..............................................................................................................................................................10
3.3 Streamflow................................................................................................................................................................11
4.0 TRENDS IN WATER QUALITY............................................................................................................................................13
4.1 Physical Parameters.................................................................................................................................................15
4.2 General Parameters .................................................................................................................................................19
4.3 Total Organic Carbon ...............................................................................................................................................21
4.4 Nutrients ...................................................................................................................................................................23
4.5 Microorganisms ........................................................................................................................................................27
5.0 SUMMARY & IMPLICATIONS .............................................................................................................................................29
5.1 Watershed impacts & Issues of Concern..................................................................................................................29
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5.2 Trends in Climate & Watershed Hydrology...............................................................................................................29
5.3 Trends in Water Quality............................................................................................................................................30
5.4 Implications to Water Treatment...............................................................................................................................31
6.0 DATA QUALITY ASSURANCE AND CONTROL.................................................................................................................33
6.1 Field Quality Control .................................................................................................................................................33
6.2 Laboratory Quality Control........................................................................................................................................34
7.0 REFERENCES.....................................................................................................................................................................35
ATTACHMENT 1........................................................................................................................................................................37
ATTACHMENT 2........................................................................................................................................................................39
ATTACHMENT 3........................................................................................................................................................................41
ATTACHMENT 4........................................................................................................................................................................43
ATTACHMENT 5........................................................................................................................................................................45
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TABLE OF FIGURES
Figure 1.1 – Map of the Upper CLP collaborative water quality monitoring network....................................................................2
Figure 2.1 – Drought conditions in Colorado on July 3, 2012. Source: www.droughtmonitor.unl.edu.........................................5
Figure 2.2 – Percent normal rainfall over the U.S. West between September 10 – 16, 2013. Part of Colorado received more
than 1000% of their normal rainfall (Source: National Oceanic and Atmospheric Administration; www.climate.gov). .................7
Figure 2.3 – Mountain pine beetle-caused mortality impacted nearly 3.4 million acres compared to 1.78 million acres impacted
by spruce beetle statewide over the last 20 years. While mountain pine beetle-caused mortality is currently considered at
background levels, spruce beetle-caused mortality continues to remain at outbreak epidemic proportions (from
https://csfs.colostate.edu/) ...........................................................................................................................................................8
Figure 2.4 – Ammonia ion wet deposition has increased throughout the United States since the NADP began in 1985 (Source:
http://nadp.slh.wisc.edu/). ............................................................................................................................................................8
Figure 3.1 – Mean baseline and current air temperatures (top), and monthly mean air temperature over the baseline and
current periods of record (bottom) reveal similar air temperature between the two periods.......................................................10
Figure 3.2 – Monthly mean precipitation totals for the baseline period compared to the recent five-year period (top) and
seasonal distribution of precipitation for the baseline period and current period (bottom). ........................................................10
Figure 3.3 – Annual precipitation totals and peak snow water equivalent measured at the Joe Wright SNOTEL......................11
Figure 3.4 – Monthly average streamflow for the baseline period compared to the recent five-year period (top) and seasonal
distribution of streamflow for the baseline period and current period (bottom)...........................................................................11
Figure 4.1 – Smoothed time-series plot for water temperature at NBH and NFG (top) and trend results for North Fork CLP river
sites............................................................................................................................................................................................15
Figure 4.2 – Smoothed time-series plot for pH on the Mainstem (top left) and North Fork (top right) CLP rivers and
corresponding trend results and estimated trend slope (bottom). ..............................................................................................16
Figure 4.3 – Smoothed time-series plot for turbidity on the Mainstem CLP river (left) and North Fork sites NDC and NFG (top
right). The corresponding trend results and estimated trend slope for all North Fork CLP rivers is located on the bottom right.
...................................................................................................................................................................................................17
Figure 4.4 – Smoothed time-series plot for specific conductivity on the Mainstem (top left) and North Fork (top right) CLP rivers
and corresponding trend results with estimated trend slope (bottom)........................................................................................18
Figure 4.5 – Alkalinity trends on the Mainstem (a) and North Fork (b) CLP river and hardness trends on the Mainstem (c) and
North Fork (d) CLP river.............................................................................................................................................................19
Figure 4.6 – Smoothed time-series plot for total dissolved solids on the Mainstem (top left) and North Fork (top right) CLP
rivers and corresponding trend results with estimated trend slope (bottom). .............................................................................20
Figure 4.7 – Smoothed time-series plot for total organic carbon on the Mainstem (top left) and North Fork (top right), and
corresponding trend results with estimated trend slope (bottom)...............................................................................................22
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Figure 4.8 – Smoothed time-series plot for total nitrogen on the Mainstem (top) and corresponding trend results with estimated
trend slope (bottom)...................................................................................................................................................................23
Figure 4.9 – Median nitrate and ammonia concentrations over the recent five-year period compared to baseline concentrations
on the Mainstem and North Fork CLP rivers. The red line indicates the City of Fort Collins Water Quality Laboratory’s
reporting limit. +s = significantly increasing step trend and + = significant increasing long-term trend .....................................24
Figure 4.10 – Smoothed time-series plot for total phosphorus on the Mainstem (left) and North Fork (right)............................25
Figure 4.11 – Median ortho-phosphate over the recent five-year period compared to baseline concentrations on the Mainstem
and North Fork CLP rivers. The red line indicates the City of Fort Collins Water Quality Laboratory’s reporting limit. +s =
significant increasing step trend and + = significantly increasing long-term trend......................................................................26
Figure 4.12 – Median total coliforms (top) and E. coli (bottom) over the recent five-year period compared to baseline
concentrations on the Mainstem and North Fork CLP rivers. + = significantly increasing trend and - = significantly decreasing
trend...........................................................................................................................................................................................27
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LIST OF TABLES
Table 2.1 – Potential raw and finished water quality impacts related to drought. Adopted from Water Research Foundation
Web Report #4324.......................................................................................................................................................................6
Table 2.2 – Potential raw and finished water quality impacts related to wildfire. Adopted from Water Research Foundation
Web Report #4324.......................................................................................................................................................................6
Table 2.3 – Potential raw and finished water quality impacts related to flooding and extreme rainfall. Adopted from Water
Research Foundation Web Report #4324....................................................................................................................................7
Table 3.1 – Summary of statistically significant climatological variables detected in the Upper CLP watershed. ......................12
Table 4.1 – Color code matrix used to present trend results from the Seasonal Mann-Kendall test indicating trend direction and
significance (p-value). ................................................................................................................................................................14
Table 4.2 – Total organic carbon removal requirements for water treatment facilities based on source water alkalinity and total
organic carbon concentrations. ..................................................................................................................................................21
Table 5.1 – Summary of water quality trends detected throughout the Upper CLP watershed over the long-term period from
2008 to 2017. (+ = increasing trend; - = decreasing trend; and +s = increasing step trend) ......................................................30
Table 6.1 – Data quality assurance statistics calculated for duplicate samples collected at PNF monitoring location in 2017. .33
Table 6.2 – Blank samples detected above their respective detection limit from 2013 to 2017. ................................................34
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UPPER CACHE LA POUDRE WATERSHED COLLABORATIVE WATER QUALITY MONITORING PROGRAM xi
LIST OF ABBREVIATIONS & ACRONYMS
% percent
BMR Barnes Meadow Reservoir Outflow (routine monitoring site)
Ca Calcium
CO3- Carbonates
cfs cubic feet per second
CHR Chambers Lake Outflow (routine monitoring site)
CLAFTCCO Cache la Poudre at Canyon Mouth Near Fort Collins Stream gage
CLP Cache la Poudre River
cfu/100 mL colony forming units per 100 milliliters
DBP Disinfection By-Product
EPA Environmental Protection Agency
FCWQL Fort Collins Water Quality Lab
FCWTF Fort Collins Water Treatment Facility
H+ Hydrogen ion
JWC Joe Wright Creek above the Poudre River (routine monitoring site)
K Potassium
LRT Laramie River Tunnel (routine monitoring site)
mmeter
Mg Magnesium
mg/L milligrams per liter
Na Sodium
NADP National Atmospheric Deposition Program
NBH North Fork of the Poudre River below Halligan Reservoir (routine monitoring site)
NDC North Fork of the Poudre River above Dale Creek Confluence (routine monitoring site)
NFG North Fork of the Poudre River below Seaman Reservoir (routine monitoring site)
NFL North Fork of the Poudre River at Livermore (routine monitoring site)
ng/L nanograms per liter
NH3-N Ammonia as nitrogen
NO2-N Nitrite as nitrogen
NO3-N Nitrate as nitrogen
NTU Nephelometric Turbidity Units
OH- Hydroxide ion
oC degrees Celsius
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PBD Poudre River at the Bellvue Diversion (routine monitoring site)
PBR Poudre River below Rustic (routine monitoring site)
PCM Pine Creek Mouth (routine monitoring site)
PJW Poudre River above the confluence with Joe Wright Creek
PNF Poudre River above the North Fork (routine monitoring site)
PO4 ortho-phosphate
ppt parts per trillion
RCM Rabbit Creek Mouth (routine monitoring site)
SCFP Soldier Canyon Filter Plant
SCWTA Soldier Canyon Water Treatment Authority
SCM Stonewall Creek Mouth (routine monitoring site)
SFC South Fork above confluence with the Mainstem (routine monitoring site)
SFM South Fork of the Poudre River above the Mainstem (routine monitoring site)
SMKT Seasonal Mann-Kendall Test
SNOTEL Snow telemetry network
SWE Snow water equivalent
T&O Taste & Odor
TKN Total Kjeldahl Nitrogen
TN Total Nitrogen
TOC Total Organic Carbon
TP Total Phosphorus
μg/L micrograms per liter
μS/cm microSeimens per centimeter
USGS United States Geological Survey
WTP Water Treatment Plant
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UPPER CACHE LA POUDRE RIVER COLLABORATIVE WATER QUALITY MONITORING PROGRAM 1
1.0 INTRODUCTION
1.1 BACKGROUND
The Upper Cache la Poudre (CLP) River is an important
source of high-quality drinking water supplies for
communities served by the City of Fort Collins Water
Treatment Facility (FCWTF), the City of Greeley-Bellvue
Water Treatment Plant (WTP), and the Soldier Canyon
Water Treatment Authority’s (SCWTA) Soldier Canyon
Filter Plant (SCFP). In the shared interest of sustaining this
high-quality water supply, the City of Fort Collins, the City
of Greeley, and the SCWTA partnered in 2007 to design the
Upper CLP Collaborative Water Quality Monitoring
Program. The Program was subsequently implemented in
spring 2008. The goal of this collaborative monitoring
program is to assist the participants in meeting current and
future drinking water treatment goals by providing up-to-
date information about water quality and trends within the
Upper CLP watershed.
Raw CLP River water quality parameters that have
historically had the most impact on treatment at the three
treatment plants include:
x turbidity
x total organic carbon (TOC)
x pH
x alkalinity
x temperature
x pathogens (Giardia and Cryptosporidium),
x taste and odor (T&O) compounds
Seasonal updates, annual water quality reports, and five-
year reports for the collaborative program are prepared by
City of Fort Collins’ Source Watershed Program staff to
keep participants informed of current issues and trends in
water quality of the Upper CLP. Seasonal updates are
provided throughout the monitoring season in the Spring,
Summer, and Fall. These updates include a summary of
precipitation, streamflow, and water quality conditions.
The purpose of annual reports is to summarize hydrologic
and water quality information for the current year, provide a
comparison with water quality from the preceding three
years, describe notable events and issues, and summarize
the results of special studies. The five-year report provides
a more in-depth analysis of long-term trends in watershed
hydrology, climate and water quality. Upper CLP updates
and reports are available on the City of Fort Collins Utilities’
Source Water Monitoring website:
(www.fcgov.com/ source-water-monitoring).
1.2 WATERSHED DESCRIPTION AND
SAMPLING LOCATIONS
Sampling efforts are divided between the Mainstem
(including the Little South Fork Cache la Poudre River) and
North Fork Cache la Poudre River watersheds. Collectively
these drainages encompass approximately 645,500 acres
of forest, other natural land types, and agricultural land. An
additional 4,700 acres, representing less than 1% of land
surface, is developed for commercial, industrial, utility,
urban or residential purposes.
The original monitoring network, established in 2008,
consisted of 20 water quality monitoring locations selected
to characterize the headwaters, major tributaries and
2 UPPER CACHE LA POUDRE WATERSHED COLLABORATIVE WATER QUALITY MONITORING PROGRAM
in the monitoring program were selected based on analysis
of historical data and aim to provide the best information
possible within current budgetary constraints. A list of
parameters is included in Attachment 3. Complete
discussions of parameter selection and sampling frequency
are provided in Sections 5.3 and 5.4, respectively, of the
program design document by Billica, Loftis and Moore
(2008). Previous year’s sampling plans are provided in
their corresponding annual reports. The 2017 sampling
plan is provided in Attachment 4 of this report.
1.4 SAMPLE COLLECTION AND
ANALYSIS
Dr. William Lewis, from the University of Colorado Boulder,
was contracted from 2008 through 2013 to perform
sampling activities for the Upper CLP monitoring program
at 17 of the 19 Mainstem and North Fork CLP sites. Staff
from the City of Fort Collins collected samples at the
remaining two locations: North Fork Poudre above the
confluence with Dale Creek (NDC) and North Fork Poudre
below Halligan Reservoir (NBH). Sampling methods,
including those for the collection of physical field
measurements for temperature, pH, conductivity, and
dissolved oxygen are documented in Section 5.5 of Billica,
Loftis and Moore (2008).
The City of Fort Collins Watershed Program coordinated
and lead all Upper CLP monitoring activities from 2013
through 2017. Sampling methods, including those for the
collection of physical field measurements for temperature,
pH, conductivity, and dissolved oxygen are documented in
the Upper Cache la Poudre Watershed Monitoring
Standard Operating Procedure (Heath 2015).
Figure 1.1 – Map of the Upper CLP collaborative water quality monitoring network.
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UPPER CACHE LA POUDRE RIVER COLLABORATIVE WATER QUALITY MONITORING PROGRAM 3
All bulk water samples were analyzed by the City of Fort
Collins Water Quality Lab (FCWQL), except for
Cryptosporidium and Giardia filter samples, which were
delivered to CH Diagnostic and Consulting, Inc., in
Berthoud, CO for analysis. The analytical methods and
detection limits for the FCWQL parameters are included in
Attachment 5.
Consistent with the quality assurance guidelines outlined in
Section 5.5 of Billica, Loftis and Moore (2008), at least ten
percent of environmental samples consist of field blanks
and field duplicate samples, which are identified in the
sampling plan (Attachment 4). Quality assurance and
quality control of field blanks and field duplicates is
discussed further in Chapter 6 of this document.
1.5 SCOPE OF FIVE YEAR REPORT
Annual and five-year reports for the Upper CLP
Collaborative Water Quality Monitoring Program are
prepared by the City of Fort Collins’ Watershed Program to
keep participants informed about current issues and trends
in water quality of the Upper CLP. The purpose of annual
reports is to summarize hydrologic and water quality
information for the current year. Annual reports highlight
significant events, issues of concern, the results of special
studies, and provide a comparison with water quality from
the preceding three years. Annual reports are available for
the years 2008-2011 and 2013-2016.
Five-year reports provide an in-depth analysis of long-term
trends in the climate, hydrology and water quality of the
Upper CLP watershed. Water quality data collected
throughout the Upper CLP watershed were analyzed for
long-term trends to determine if concentrations increased,
decreased or stayed the same over the ten-year period of
record from 2008 to 2017. This report documents 1)
watershed impacts and issues of concern; 2) significant
trends in climate, hydrology, and water quality in the Upper
CLP watershed; 3) potential sources of pollution and/or
watershed disturbances influencing water quality trends;
and 4) a summary of significant findings and implications to
water treatment. The last five-year report was published in
2013, which reviewed trends over the five-year period of
record from 2008 to 2012 (Oropeza and Heath, 2013).
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UPPER CACHE LA POUDRE RIVER COLLABORATIVE WATER QUALITY MONITORING PROGRAM 5
2.0 WATERSHED
IMPACTS & ISSUES
OF CONCERN
2.1 CLIMATE CHANGE
Climate change is one of the most critical issues related to
watersheds and water supplies of the Colorado Front
Range. It is predicted that warmer temperatures will result
in changes to the water cycle, which will influence the
watersheds that collect, store, and deliver clean water for
consumptive and non-consumptive uses. The most serious
consequences of climate change on Colorado watersheds
include:
x Changes in precipitation patterns, timing and type;
x Shifts in timing and intensity of runoff and
streamflow;
x Increases in severity and frequency of droughts
and wildfires;
x Increases in frequency and intensity of forest
insect infestations.
Colorado is already limited on its water resources and
extremely vulnerable to increasing extremes due to climate
change. Many of the consequences of climate change will
directly impact drinking water supplies. Precipitation
patterns in Colorado vary over space and time. Changes
in precipitation patterns, timing, and type may result in
periods of extended drought, as well as periods of intense
precipitation events. These patterns result in extreme
variability from year to year. Most of Colorado’s
precipitation occurs during the winter months. Shifts in the
timing of precipitation, in addition to more precipitation
falling as rain than snow, will add to the uncertainty in the
timing and intensity of runoff and streamflow. The onset of
streamflow from melting snow is projected to shift earlier in
the spring resulting in reduced runoff in the late summer.
These climate-driven changes to the water cycle present
many challenges to water managers making it difficult to
estimate the quantity and quality of water available to meet
current and future water needs.
In combination with changes to water quantity, changes to
water quality may also occur because of climate change-
driven impacts to Colorado watersheds. The increase in
the severity, frequency, and intensity of droughts, wildfires,
and insect infestations can result in dramatic changes to the
land cover of Colorado’s watersheds, directly impacting
water quality. Droughts are the leading cause of wildfires
and therefore, with the occurrence of more prolonged
droughts come increased frequency of wildfires. Wildfires
impact watershed hydrology by changing ecosystem
resources such as vegetation and soils resulting in
increased pollution to drinking water supply.
2.2 DROUGHT AND WILDFIRE
Extreme drought conditions were observed throughout the
State of Colorado and the Upper CLP watershed in 2012.
The maximum amount of water stored in the snowpack
(snow water equivalent) in 2012 at the Joe Wright Snow
Telemetry station near Cameron Pass was 57% of normal
and occurred nearly two months earlier than expected.
Colorado experienced its warmest March on record and
abnormally hot and dry conditions persisted throughout the
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in the Upper CLP watershed. Potential impacts of drought
on raw and treated water quality are summarized in Table
2.1.
The exceptionally hot and dry conditions in 2012 (Figure
2.1) lead to extreme wildfire conditions throughout
Colorado. The Upper CLP watershed was impacted by two
major wildfires in 2012. The Hewlett Gulch Fire (May 14-
22) burned 7,685 acres in dense Ponderosa Pine forest
stands on the north-facing slopes, as well as shrub and
grasslands that occupied much of the south-facing aspects.
The burned area includes sub-watersheds that drain both
to the Mainstem and into Seaman Reservoir on the North
Fork.
The High Park Fire (June 9 - July 2) burned 87,415 acres
of primarily forested landscape characterized by Ponderosa
and Lodgepole Pine at the lower elevations and mixed
conifer species at the upper elevations. To a lesser degree,
shrublands, grasslands and riparian areas were also
impacted. The burned area includes numerous sub-
drainages that are tributaries to the Mainstem and the
South Fork.
The 2012 wildfires caused dramatic changes to land cover
within the Upper CLP watershed that had an immediate
effect on watershed hydrology and water quality within and
downstream of the burn scars. The disturbance caused an
increase in streamflow and sediment erosion into streams
draining burned sub-basins specifically during and following
high-intensity storm events. The loss of vegetative cover
altered the cycling of water, carbon, nutrients and other
elements, directly influencing water quality in the Poudre
River. Potential impacts on raw and treated water quality
from wildfires are summarized in Table 2.2.
Upper CLP monitoring sites that were impacted by the
wildfires were limited to the middle to lower elevations of
the watershed and included the South Fork above the
Mainstem Confluence, SFC, the Poudre below the South
Fork (PSF), PNF, the North Fork below Seaman Reservoir
(NFG), and the Poudre at the Bellvue Diversion (PBD)
(Figure 1.1). Routine data collected from these monitoring
locations (pre- (2008 to 2012) and post-wildfire (2012-
2017)) are valuable for evaluating the impacts of wildfire on
CLP water quality (non-event based) and watershed
recovery.
Raw Water Quality Finished Water Quality
Increased nutrients,
algae, cyanobacteria,
MIB, geosmin
Taste and odor
Potential for cyanotoxins
Color and turbidity Color and turbidity
Increased metals Manganese, color
Increased TOC DBPs (THMs and HAAs)
Decreased DO
Increased hardness
Increased alkalinity DBPs (THMs and HAAs)
2.3 FLOODING
In September of 2013, the Colorado Front Range and
adjacent foothills experienced a period of intense rainfall
leading to severe flooding in streams and rivers throughout
UPPER CACHE LA POUDRE RIVER COLLABORATIVE WATER QUALITY MONITORING PROGRAM 7
In the foothills of Larimer County, 15 inches of rainfall was
recorded over this period with areas in Fort Collins
receiving over 12 inches of rain. Higher intensities and
rainfall depth likely occurred at higher elevations in the
Upper CLP watershed. As a result, extreme flooding
occurred within the Cache la Poudre watershed with a
return interval ranging from a 25 to 50-year flood on the
CLP river (Yochum, 2015). The flood peak at the Canyon
Mouth was nearly five times greater than the average
snowmelt peak and measured 9,730 cubic feet per second
(cfs) on September 13th. Flood waters began to recede
following the flood peak and returned to baseflow (low-flow)
conditions by early October. Baseflows remained higher
than average in the years following the flood and appeared
to return to near normal conditions in 2016. Potential
impacts related to flooding and extreme rainfall events are
outlined in Table 2.3.
2.4 FOREST INSECTS AND DISEASE
Native forest insects and disease are common in
Colorado’s forests and play an important role in forest
ecology and maintaining healthy, resilient forests that
provide clean water to lakes, streams and rivers. Over the
past two decades several forest insects and diseases have
impacted Colorado’s forests.
The mountain pine beetle (MPB), a native bark beetle that
infests all pine species, impacted over 3 million acres of
Colorado’s forest over the past two decades. The mountain
pine beetle epidemic began in 1996 and tree mortality
peaked in 2008 at 1.2 million trees (Figure 2.3). Over the
past 10 years, pine beetle-caused tree mortality steadily
decreased to less than 900 acres of native pine forest
affected in 2017 (Colorado State Forest Service, 2017). A
large portion of the tree mortality caused by the mountain
pine beetle was concentrated in lodge pole pine forest in
north-central Colorado including portions of the Upper CLP
watershed.
The spruce beetle has destroyed 1.78 million acres since
1996 and has been Colorado’s most common forest insect
over the past six years, destroying more than 200,000
acres of high-elevation Engelmann spruce forest. The
highest spruce beetle-caused tree mortality was observed
in 2014 at over 400,000 acres (Figure 2.3). State-wide tree
morality has been on the decline over the past three years
(Colorado State Forest Service, 2017). In 2017, the
Colorado State Forest Service identified significant
infestations in Larimer County and noted the potential for
expanding outbreaks in susceptible Engelmann spruce
forests in the northern portion of the state suggesting the
potential for future infestations and tree mortality in the
Upper CLP watershed.
Douglas-fir beetle has also infested dense, mature, and
drought stricken Douglas-fir forests across Colorado, but
the impact and extent is much less compared to the
mountain pine beetle and spruce beetle infestations.
2.5 AIR POLLUTION
Air pollution along Colorado’s Front Range and from other
areas may impact water quality in the Upper CLP
watershed through a process called atmospheric
deposition. Atmospheric deposition occurs when pollutants
8 UPPER CACHE LA POUDRE WATERSHED COLLABORATIVE WATER QUALITY MONITORING PROGRAM
precipitation (wet deposition) or as dry particles and gases
(dry depositions). Acidic deposition has been the most
widely studied form of atmospheric deposition, which has
led to acidification of surface waters from acid compounds
(sulfur and nitrogen) and other chemicals. The main source
of sulfur dioxide to the atmosphere is large powerplants and
the source of nitrogen oxide and ammonium emissions
include vehicle emissions, oil and gas development, and
agricultural practices.
The National Atmospheric Deposition Program (NADP;
http://nadp.slh.wisc.edu/) is a cooperative effort between
private, governmental and non-profit agencies that
measures precipitation chemistry (wet deposition)
throughout the United States with the goal of monitoring the
chemistry of precipitation to determine changes over time.
Atmospheric deposition has been monitored near the
headwaters of the Cache la Poudre River in Rocky
Mountain National Park since the early 1980s through the
National Atmospheric Deposition Program.
Long-term records from monitoring stations in Rocky
Mountain National Park and throughout Colorado show
decreasing trends in sulfate since the early 1990s because
of efforts to reduce emissions established under the 1990
Clean Air Act Amendments. The reduction in sulfur dioxide
emissions has lessened the amount of sulfuric acid in the
atmosphere and lead to declines in precipitation acidity and
acidic deposition into Colorado’s watersheds (Mast, 2011).
In contrast, trends in nitrogen species (nitrate and
ammonium) have been less sensitive to emission
reductions and voluntary management strategies aimed at
limiting nitrogen to the atmosphere. Increasing trends
were observed in ammonium with the largest increase near
agricultural and urban areas in eastern Colorado (Mast,
2011; Figure 2.4). It is expected that these trends will
continue in the future because of projected population
growth along the Colorado Front Range and increasing oil
and gas production in Colorado.
Figure 2.3 – Mountain pine beetle-
caused mortality impacted nearly 3.4
million acres compared to 1.78 million
acres impacted by spruce beetle
statewide over the last 20 years. While
mountain pine beetle-caused mortality
is currently considered at background
levels, spruce beetle-caused mortality
continues to remain at outbreak
epidemic proportions (from
https://csfs.colostate.edu/)
Figure 2.4 – Ammonia ion wet deposition has increased
throughout the United States since the NADP began in 1985
(Source: http://nadp.slh.wisc.edu/).
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3.0 WATERSHED
HYDROLOGY AND
CLIMATE
The hydrology of the Upper CLP plays an important role in
regulating water quantity and quality. Precipitation events
and snowmelt runoff largely control the quantity and timing
of deliveries of material to the river, and the amount of water
in the system at a given time influences the concentration
of most water quality constituents. Changes to the timing,
magnitude, and duration of snowmelt runoff and the effects
on water quality have implications on water treatment
operations that may need to be addressed in the future to
continue to maintain a high-quality water supply to the
public.
Evaluating Trends Short-Term and Long-Term Data
Short-term trends are presented for the most recent five
years of data from 2013 to 2017 (current) and compared to
baseline data from 2008 to 2012 (baseline). Annual and
monthly mean air temperature, precipitation, and
streamflow were calculated for the current period of record
and compared to the baseline period of record.
Long-term trends are presented for the combined ten-year
period of record from 2008 to 2017. The Seasonal Mann-
Kendall test (SMKT) was used to evaluate long-term trends
in air temperature, precipitation and streamflow. The SMKT
was performed on 1) monthly average minimum, maximum
and mean air temperature calculated from daily average
minimum, maximum and mean air temperatures; 2)
monthly cumulative precipitation calculated from daily
precipitation; and 3) monthly mean streamflow calculated
from daily average streamflow. The Mann-Kendall test
was used to evaluated annual and seasonal trends.
Seasons were defined as winter (December – February),
spring (March – May), summer (June – August), and fall
(September – November).
Statistical significance was determined to the 95%
confidence level (S
10 UPPER CACHE LA POUDRE WATERSHED COLLABORATIVE WATER QUALITY MONITORING PROGRAM
SNOTEL. Trend analyses of air temperature data collected
at the Cache la Poudre at Canyon Mouth near Fort Collins
(CLAFTCCO) streamflow monitoring station revealed no
discernable trends.
3.2 PRECIPITATION
Annual mean precipitation over the five-year period was
slightly greater than baseline annual mean precipitation.
The five-year annual mean precipitation was 46.4 inches
compared to 45.3 inches. The higher precipitation that fell
over the five-year period was due to wetter conditions in the
winter, spring, and fall seasons (Figure 3.2). Monthly mean
precipitation during these seasons was greater in all
months except April and October. Less precipitation fell
over the summer season with notably lower precipitation in
the months of June and July (Figure 3.2).
There were no significant long-term trends in annual,
monthly, or seasonal precipitation over the long-term period
of record. Total precipitation was variable from year to year.
The highest precipitation was measured in water year 2011
with a total 64.4 inches of precipitation falling on the Upper
CLP watershed. In contrast, only 32.2 inches of
precipitation was measured in 2012 leading to severe
drought conditions and wildfires in the Upper CLP
watershed.
There were two notable long-term trends identified at the
90% confidence level for significance (p = 0.10). The
maximum amount of water contained within the snowpack
(peak snow water equivalent) showed a decreasing trend
over the long-term period of record at a rate of 1.03 inches
per year. Although there was considerable variability in
peak SWE from year to year (Figure 3.3), the trend
suggests higher elevations of the Upper CLP watershed
may receive less snowfall over the snow accumulation
season into the future. Another notable decreasing trend
was detected in the peak SWE to precipitation ratio
implying precipitation patterns may be shifting in the Upper
CLP watershed with more precipitation falling as snow or
rain in the spring following peak SWE or as rain in the fall.
Figure 3.1 – Mean baseline and current air temperatures (top),
and monthly mean air temperature over the baseline and
current periods of record (bottom) reveal similar air temperature
between the two periods.
Baseline Current
40
30
20
10
0
TEMPERATURE, degrees F
Dec
Nov
Oct
Sep
Aug
Jul
Jun
May
Apr
Mar
UPPER CACHE LA POUDRE RIVER COLLABORATIVE WATER QUALITY MONITORING PROGRAM 11
3.3 STREAMFLOW
The five-year annual mean streamflow was greater than
baseline streamflow conditions. Annual mean streamflow
during the five-year period of record was 513 cubic feet per
second (cfs) compared to the baseline of 326 cfs. The
higher streamflow over the five-year period was driven by
notably higher streamflow in all months except July (Figure
3.4).
A shift in seasonal flow contributions was observed over the
five-year period. The proportion of water delivered during
the winter season was similar compared to baseline
conditions, but a smaller amount of water was measured
during the summer season, notably in the month of July.
The amount of water delivered over the spring and fall
seasons was considerably greater over the five-year period
of record (Figure 3.4). Five-year monthly mean streamflow
was more than two times higher in the spring months of
March, April, and May (Figure 3.4). Streamflow during the
fall months was also greater over the five-year period likely
due to extreme precipitation and flooding in September of
2013 and elevated baseflows in the following years. As a
result, 500,000 more acre-feet of water was measured over
the five-year period of record compared to baseline.
Streamflow significantly increased in the Upper CLP
watershed over the long-term period of record (2008-2017).
A significant increase was detected in both monthly mean
streamflow and streamflow during the winter season.
Monthly mean streamflow increased at a rate of 13 cfs per
year, while winter streamflow increased at a rate of 9 cfs
per year (Table 3.1). An increasing trend in spring
streamflow was detected at a rate of 7 cfs per year, but this
trend was not statistically significant (p=0.08).
There were no significant trends in the magnitude or timing
of peak streamflow. Peak streamflow over the long-term
period was higher than the historic (1881-2017) peak in
seven out of 10 years averaging 988 cfs higher than the
historic average peak (2,000 cfs). The timing of peak
streamflow occurred an average of 1.3 days later than the
historic average (June 11). The latest peak was observed
on July 1, 2011 (20 days late) and the earliest peak was
observed on May 31, 2014 (11 days early).
Figure 3.3 – Annual precipitation totals and peak snow water
equivalent measured at the Joe Wright SNOTEL.
2017
2016
2015
2014
2013
2012
2011
2010
2009
2008
70
60
50
40
30
20
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Paramater Test Statistic Season Trend Direction Trend Estimate Significance
(p-value)
Streamflow Monthly Mean
Annual Increasing 13 cfs per year 0.01
Winter Increasing 9 cfs per year <0.01
Precipitation
Peak SWE Water Year Decreasing 1.03 inches per year 0.10
SWE/Precipitation
Ratio Water Year Decreasing 0.02 inches per year
0.07
Temperature
Monthly Mean
Annual Increasing 0.24°F (0.13°C) per year 0.01
Winter Increasing 0.32°F (0.18°C) per year 0.02
Monthly Minimum
Annual Increasing 0.32°F (0.18°C) per year <0.01
Winter Increasing 0.37°F (0.21°C) per year 0.05
Table 3.1 – Summary of statistically significant climatological variables detected in the Upper CLP watershed.
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4.0 TRENDS IN
WATER QUALITY
Water quality data collected throughout the Upper CLP
watershed were analyzed for long-term trends to determine
if concentrations increased, decreased or stayed the same
over the ten-year period of record from 2008 to 2017.
Analysis of long-term water quality data for trends provides
useful information about short and long-term impacts to
water quality from watershed disturbances and pollution
that may influence water treatment processes and direct
watershed management now and in the future.
Preliminary data analyses
Preliminary data analyses were conducted to initially
identify and characterize potential trends in the Upper CLP
long-term data set. Time-series scatterplots were
evaluated and data smoothing techniques were applied to
further uncover general tendencies. Two types of trends
were identified in this process: monotonic trends and step
trends. Monotonic trends are defined as a gradual,
continuous rate of change (increasing or decreasing) in the
data over time and step trends are defined as an abrupt
shift (up or down) in the data at a certain point in time.
Preliminary data analyses also provided additional
information required for selecting the most robust trend test.
Trend tests are generally categorized as parametric and
nonparametric, and the statistical power of these analyses
depends on the distribution of the data. Parametric trend
tests are considered the most powerful analyses for
normally distributed data sets and nonparametric tests are
used on data where the assumption of normality for
parametric statistics is not met (Lettenmaier 1976, Hirsch
et al. 1991, Thas et al. 1998). Normality tests verified data
distributions of water quality variables were not normal
(p<0.01) and a nonparametric test would provide the most
powerful and robust trend analyses.
Trend Analyses
Based on preliminary data analyses discussed above, two
trend tests were selected to detect and quantify trends in
water quality concentrations throughout the Upper CLP
watershed. Monotonic trends were evaluated with the
Seasonal Mann-Kendall Test (SMKT). Water quality in the
Upper CLP watershed exhibits strong seasonal patterns
and the SMKT accounts for variability in water quality due
to seasonality (Helsel and Hirsch, 1992). The SMKT was
performed on monthly concentrations measured over the
ten-year period of record (2008 to 2017) with seasons
defined by month. Bimonthly data collected in the months
of April, May, and June were aggregated by month and a
monthly median value was calculated for trend analyses.
The output of the test provides a p-value and overall
measure of the rate of change or trend slope. Statistical
significance was determined to the 95% confidence level (p
14 UPPER CACHE LA POUDRE WATERSHED COLLABORATIVE WATER QUALITY MONITORING PROGRAM
Presentation of Results
Presentation of the results focuses primarily on monitoring
sites located directly on the Mainstem and North Fork CLP
rivers that are considered representative of water quality
conditions throughout the Mainstem CLP watershed;
however, data collected from monitoring sites located on
tributaries to the Mainstem and North Fork CLP rivers were
analyzed and tested for trends. Significant and notable
findings from these sites are also presented. A full list of
monitoring sites, abbreviations and descriptions is available
in Attachment 2. Finalized raw data are available upon
request from the City of Fort Collins Watershed Program.
The graphics presented in the following sections of this
report include time-series scatterplots customized with a
smoothed line fit to the data. Data were smoothed using
the locally weighted scatterplot smoothing (LOWESS)
technique. The degree of smoothing (0-1) was set to 0.25
and the influence of outliners (0-10) was set to 10. The
larger the weights, the more the smoothed values follow the
data and the smaller the weights, the less jagged the
pattern is in the smoothed values.
The colored bar graphs presented below the smoothed
time-series graphs summarize trend test results from the
SMKT. Bar graphs include the trend slope (rate of change
over time), trend direction (increasing or decreasing), and
statistical significance (p<0.05 and p<0.10). The trend
slope is plotted on the y-axis and monitoring locations are
on the x-axis. A positive value specifies an increasing trend
and a negative value specifies a decreasing trend.
Statistical significance and trend direction are color coded.
Refer to table 4.1 for color codes and additional information
for interpreting the results from monotonic trend analyses.
Trend tests detect significant trends and provide a
measured rate of change, but do not provide insight to the
cause of the trend. Interpretation of potential causes were
based on technical expertise and local knowledge
regarding specific events and impacts to watershed
hydrology and land use over the period of record.
Color Code Trend
direction
Statistical Significance
Increasing
95% confidence interval
p-value < 0.05
Decreasing
Increasing
90% confidence interval
p-value < 0.10
Decreasing
No Trend Not statistical significant
p-value > 0.10
Table 4.1 – Color code matrix used to present trend results
from the Seasonal Mann-Kendall test indicating trend direction
and significance (p-value).
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Attachment: 2017 Five Year Upper Poudre River Water Quality Report (8063 : Water Resources, Watershed, and Water Quality Protection
UPPER CACHE LA POUDRE RIVER COLLABORATIVE WATER QUALITY MONITORING PROGRAM 15
4.1 PHYSICAL PARAMETERS
Water Temperature
Long-term trends were detected below Halligan and
Seaman Reservoir in the North Fork CLP watershed.
Water temperature at these monitoring sites (NBH and
NFG) significantly increased 0.18°C (0.32°F) per yearand
0.19°C (0.34°F) per year over the long-term (Figure 4.1).
There were no trends observed in water temperature in the
Mainstem CLP watershed. The noticeable decrease in
temperature after 2013 was observed throughout the
watershed and may be attributed to the 2013 flood event.
pH
pH is a measure of the amount of free hydrogen (H+) and
hydroxide (OH-) ions in water and is measured on a
logarithmic scale ranging from 0 to 14. Water with a pH
near 7 is considered neutral, with more acidic conditions
occurring below 7 and more basic, or alkaline, conditions
occurring above 7. pH is an important water quality
parameter to monitor because it influences the solubility
and biological availability of chemical constituents,
including nutrients and heavy metals.
pH increased at nearly all monitoring sites throughout the
Upper CLP watershed over the long-term monitoring period
(Figure 4.2). There were no trends detected at the highest
elevation monitoring sites on Joe Wright Creek (CHR) and
the Poudre River above the confluence with Joe Wright
Creek (PJW). pH significantly decreased at BMR, but this
trend did not influence pH trends downstream at JWC
where pH significantly increased 0.03 units per year.
Significantly increasing trends continued downstream with
the greatest changes in pH measured on the Mainstem
CLP river above and below the confluence with the North
Fork CLP river (PNF and PBD). pH increased 0.07 units
per year over the long-term period at PNF and slightly
higher at PBD (Figure 4.2).
pH increased throughout the North Fork CLP watershed,
but at a slower rate compared to the Mainstem CLP
watershed. pH significantly increased 0.03 units per year
at most sites, including Rabbit Creek (RCM) and Stonewall
Creek (SCM). Although there was a slight increase in pH
measured at PCM there the trend was not significant
(Figure 4.2).
Turbidity
Turbidity is a measurement of the amount of light capable
of passing through water. This water quality parameter is
often monitored to track changes in water clarity, which is
influenced by the presence of algae and/or suspended
solids introduced to surface waters through various land
use activities, including runoff and erosion, and urban storm
water runoff and drainage from agricultural lands. Turbidity
concentrations can signal changes in land use activity.
For water treatment, turbidity is an important indicator of the
amount suspended material that is available to harbor
pollutants such as heavy metals; bacteria and other
pathogens; nutrients; and organic matter.
Step trends were measured at monitoring sites from the
South Fork CLP river (PSF) downstream to the Mainstem
CLP river below the confluence with the North Fork (PBD).
Median turbidity values over the recent five-year period
16 UPPER CACHE LA POUDRE WATERSHED COLLABORATIVE WATER QUALITY MONITORING PROGRAM
monitoring sites upstream of the wildfire burn scar
suggesting that the abrupt increase in turbidity observed in
2013 was caused by post-fire erosion impacts. The
decreasing trend in recent years provides evidence of
watershed recovery (Figure 4.3).
Trend analyses of the recent five-year period of record
detected significantly decreasing trends at wildfire impacted
sites suggesting a return to baseline turbidity conditions.
The highest turbidity was measured in 2013 and steadily
decreased to near baseline conditions in 2017. Turbidity
decreased 0.6 NTU per year at PNF and PBD over this
period. The flood of 2013 likely accelerated the recovery to
pre-fire turbidity levels by scouring the streambed. Turbidity
also significantly increased 0.17 NTU per year at LRT in the
Mainstem CLP watershed, but this trend did not influence
water quality downstream at PBR.
Long-term trends were measured at two monitoring sites in
the North Fork CLP watershed. Turbidity significantly
increased 0.28 NTU per year on the North Fork CLP river
below Seaman Reservoir at NFG (Figure 4.3). This trend
did not translate downstream to the Poudre River at
Greeley’s water intake at PBD. A notable increase in
turbidity was also observed on the North Fork CLP above
Halligan Reservoir at NDC. Although there is less certainty
9
8
7
2008 2013 2018
9
8
7
2008 2013 2018
9
8
7
03JWC
pH UNITS
04PJW
06PBR 08PSF
09PNF 10PBD
9
8
7
2008 2013 2018
9
8
7
2008 2013 2018
9
8
7
11NDC
pH UNITS
12NBH
13NRC 17NFL
18NFG
PBD
PNF
PSF
UPPER CACHE LA POUDRE RIVER COLLABORATIVE WATER QUALITY MONITORING PROGRAM 17
in this trend it will be important to continue to track this in
the future as increased turbidity may indicate increased
sediment loading into Halligan Reservoir. No trends were
observed on the North Fork CLP or tributaries between
Halligan and Seaman Reservoirs.
Specific Conductivity
Conductivity is an index of dissolved ionic solids in water,
and hardness is an index of the total calcium (Ca) and
magnesium (Mg) in water. Alkalinity is a measure of the
effective acid buffering capacity of water, and is derived
from the dissociation of mineral carbonates (CO3-),
bicarbonates (HCO3-), and hydroxides (OH-). Conductivity,
hardness, and alkalinity are influenced by local geology, as
well as other dissolved constituents derived from land use
practices throughout the watershed.
In the Mainstem CLP watershed, long-term trends were
identified at monitoring sites located above the wildfire burn
scar and step trends were identified at monitoring sites
located within the wildfire burn scar. Specific conductivity
significantly decreased 0.5 μS/cm per year at PJW with
notable decreasing trends at CHR and LRT (-0.28 and -
0.90 μS/cm per year) over the long-term monitoring period
(Figure 4.4).
Step trends were measured at monitoring sites located
within the wildfire burn scar. Specific conductivity was
significantly higher over the current five-year period
compared to baseline conditions at PNF. The abrupt
increase in specific conductivity was first observed in 2013
and continued through 2017. Median specific conductivity
measured over this period was 1.5 times greater than
baseline conditions (Figure 4.4). The elevated specific
conductivity provides further evidence of post-fire effects
that continue to impact water quality five years after the
wildfire (Figure 4.4).
Specific conductivity increased over the long-term record at
higher elevation monitoring sites in the North Fork CLP
watershed and step trends were observed at mid- and low-
elevation monitoring sites. Specific conductivity
significantly increased 1.35 μS/cm per year at NDC and
1.83 μS/cm per year at NBH.
Step trends were observed from NRC downstream to NFG
with an abrupt increase in 2012 followed by an abrupt
2008 2013 2018
10
8
6
4
2
0
2008 2013 2018
11NDC
TURBIDITY, NTU
18NFG
NFG
NFL
NRC
NBH
NDC
0.4
18 UPPER CACHE LA POUDRE WATERSHED COLLABORATIVE WATER QUALITY MONITORING PROGRAM
decrease in 2013. These shifts are likely correlated with
streamflow variability and the concentrating effects of low
streamflow caused by drought conditions in 2012 and
dilution effects of high streamflow following the 2013 flood
event. Over the long-term period of record a decreasing
trend was detected at these monitoring sites. Specific
conductivity significantly decreased 5.25 μS/cm per year at
NRC and 4.98 μS/cm per year at NFL (Figure 4.4). The
slight decrease in the rate of change between NRC and
NFL may be influenced by the inflowing waters of Stonewall
Creek, which have characteristically higher specific
conductivity. Specific conductivity significantly decreased
3.54 μS/cm per year at NFG and this trend may have
abated the wildfire impacts downstream as no trends were
observed at PBD (Figure 4.4).
120
80
40
2008 2013 2018
120
80
40
2008 2013 2018
120
80
40
03JWC
SPECIFIC CONDUCTIVITY, uS/cm
04PJW
06PBR 08PSF
09PNF 10PBD
400
200
0
2008 2013 2018
400
200
0
2008 2013 2018
400
200
0
11NDC
SPECIFIC CONDUCTIVITY, uS/cm
12NBH
13NRC 17NFL
18NFG
NFG
NFL
NRC
NBH
NDC
5.0
2.5
0.0
-2.5
-5.0
uS/cm/yr
PBD
UPPER CACHE LA POUDRE RIVER COLLABORATIVE WATER QUALITY MONITORING PROGRAM 19
4.2 GENERAL PARAMETERS
Alkalinity and Hardness
Long-term trends in alkalinity and hardness were nearly
identical to specific conductivity (Figure 4.4). Significant
trends were detected in both the Mainstem and North Fork
CLP watersheds, but there was no indication of watershed
wide changes except for monitoring locations impacted by
wildfire.
Hardness significantly decreased at BMR and PJW over
the long-term period, but these trends did not translate
downstream (Figure 4.5b). Step trends were observed at
monitoring sites located within and downstream of the
wildfire burn scar. Like specific conductivity, median
alkalinity and hardness concentrations were 1.5 – 2 times
greater over the recent five-year period compared to
baseline conditions and remained elevated through 2017.
Alkalinity and hardness significantly increased above and
below Halligan Reservoir (NDC and NBH, respectively).
Decreasing trends were detected at NRC and SCM, but
these trends were not detected downstream at NFL or NFG
(Figure 4.5).
Total Dissolved Solids
The total dissolved solids (TDS) concentration provides a
qualitative measure of dissolved ions and comprise
inorganic salts (calcium, magnesium potassium, sodium,
bicarbonates, chlorides, and sulfates) and a small portion
of organic matter. Sources of TDS in surface water consist
of natural weathering and erosion of geologic material,
mining, industrial and sewage effluent, and agriculture.
Elevated TDS concentrations in drinking-water sources do
not pose a health risk, but high levels can cause aesthetic
risks including corrosion, salty or brackish taste, and scale
formation. Because of these potential risks the
Environmental Protection Agency established a secondary
drinking water standard for TDS. Elevated TDS
concentrations may also be used as an indicator of
elevated ions; some of which have primary or secondary
drinking water standards.
A watershed wide increase was observed in total dissolved
solids throughout the Mainstem CLP watershed over the
long-term monitoring period. Significantly increasing trends
were identified at all sites along the Mainstem CLP river and
on Joe Wright Creek at JWC. Concentrations gradually
Figure 4.5 – Alkalinity trends on the Mainstem (a) and
North Fork (b) CLP river and hardness trends on the
Mainstem (c) and North Fork (d) CLP river
PBD
PNF
PSF
PBR
PJW
JWC
0.8
0.6
0.4
0.2
0.0
mg/L/yr
NFG
20 UPPER CACHE LA POUDRE WATERSHED COLLABORATIVE WATER QUALITY MONITORING PROGRAM
increased at mid- and high-elevation monitoring sites at a
rate of 1.1 mg/L per year (Figure 4.6). TDS at these
monitoring sites steadily increased in the years following
the 2013 flood highlighting the persisting impacts of
extreme flooding on water quality.
Step trends were identified at monitoring sites from the
South Fork CLP river downstream and within the wildfire
burn scar. Median TDS concentrations measured over the
recent five-year period were 20 mg/L greater at PNF and
PBD compared to baseline conditions (Figure 4.6). Total
dissolved solids remained elevated in 2017 at PNF and
PBD, but concentrations at PBD appear to be returning to
baseline conditions.
Total dissolved solids significantly increased above and
below Halligan Reservoir (NDC and NBH, respectively),
and on Stonewall Creek over the long-term monitoring
record in the North Fork CLP watershed. Step trends were
observed from NRC downstream to NFG with an abrupt
increased in 2012 followed by an abrupt decreased in 2013.
Analogous to the trends observed in specific conductivity,
the shifts in TDS are likely correlated with streamflow
variability and the concentrating effects of low streamflow
caused by drought conditions in 2012 and dilution effects of
high streamflow following the 2013 flood event.
60
40
2008 2013 2018
60
40
2008 2013 2018
60
40
03JWC
TOTAL DISSOLVED SOLIDS, mg/L
04PJW
06PBR 08PSF
09PNF 10PBD
PBD
PNF
PSF
PBR
PJW
JWC
2.9
2.3
1.7
1.1
0.5
mg/L/yr
240
160
80
2008 2013 2018
240
160
80
2008 2013 2018
240
160
UPPER CACHE LA POUDRE RIVER COLLABORATIVE WATER QUALITY MONITORING PROGRAM 21
4.3 TOTAL ORGANIC CARBON
Total organic carbon (TOC) is a measure of the total
concentration of dissolved and particulate organic matter in
water. TOC is derived from both terrestrial and aquatic
sources. Terrestrial TOC originates from soils and plant
materials that are leached and/or delivered to surface
waters during storms and spring snowmelt runoff, whereas
aquatic-derived TOC originates from algal production and
subsequent decomposition within surface waters.
Total organic carbon is an important indicator of water
quality, particularly as it relates to water treatment. Water
treatment requires the effective removal of TOC because
the interaction between residual TOC and chlorine can form
regulated disinfection by-products (DBPs). DBPs are
strictly regulated due to their carcinogenic potential.
Increases in source water TOC concentrations pose
concern due to the potential for higher residual TOC (post-
filtration) and increased DBP formation potential. In
addition, increased levels of TOC in source waters require
additional removal requirements at the water treatment
facility based on alkalinity levels (Table 4.2).
TOC
(mg/L)
Source water alkalinity
(mg/L as CaCO3)
<60 60-120 >120
2-4 40% 30% 20%
4-8 45% 35% 25%
>8 50% 40% 30%
Total organic carbon concentrations gradually increased
throughout the Mainstem CLP watershed over the long-
term period of record. Significantly increasing trends were
measured at all monitoring sites. The greatest increase
was measured at the Barnes Meadow outflow diversion
(BMR) where TOC concentrations increased 0.29 mg/L per
year. TOC concentrations on the Mainstem CLP river
changed at a slower rate. The greatest change was
observed at the highest elevation monitoring site at PJW.
Although, the rate of change was similar at mid- to lower-
elevation monitoring sites (PBR to PNF), there was a slight
increase in the trend slope moving downstream (Figure
4.7).
In the North Fork CLP watershed, TOC concentrations
have been steadily decreasing over the most recent five-
year period, but significant trends were only detected on
Stonewall Creek and on the North Fork CLP river below
Seaman Reservoir at NFG. TOC significantly increased
0.07 mg/L per year at SCM and significantly decreased
0.06 mg/L per year at NFG (Figure 4.7). It appears the
decreasing TOC trend at NFG had a slight influence on
downstream at PBD where the rate of change over the long-
term period was slightly less than PNF upstream (0.08 mg/L
per year and 0.10 mg/L per year; Figure 4.7).
There was a short-term decrease in TOC at all monitoring
sites throughout the Upper CLP watershed in 2012 further
highlighting the impacts of severe drought on water quality.
In contrast to other water quality variables, severe drought
and resultant low snowpack and streamflow limit the
delivery of organic carbon to surface waters. Potential
22 UPPER CACHE LA POUDRE WATERSHED COLLABORATIVE WATER QUALITY MONITORING PROGRAM
9
6
3
2008 2013 2018
9
6
3
2008 2013 2018
9
6
3
11NDC
TOTAL ORGANIC CARBON, mg/L
12NBH
13NRC 17NFL
18NFG
NFG
NFL
NRC
NBH
NDC
0.1
0.0
-0.1
mg/L/yr
Figure 4.7 – Smoothed time-series plot for total organic carbon on the Mainstem (top left) and North Fork (top right), and corresponding
trend results with estimated trend slope (bottom).
9
6
3
2008 2013 2018
9
6
3
2008 2013 2018
9
6
3
03JWC
TOTAL ORGANIC CARBON, mg/L
04PJW
06PBR 08PSF
09PNF 10PBD
PBD
PNF
PSF
PBR
PJW
JWC
0.12
0.08
0.04
0.00
mg/L/yr
2.6
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Attachment: 2017 Five Year Upper Poudre River Water Quality Report (8063 : Water Resources, Watershed, and Water Quality Protection
UPPER CACHE LA POUDRE RIVER COLLABORATIVE WATER QUALITY MONITORING PROGRAM 23
4.4 NUTRIENTS
Nutrients are an important component of source water
quality monitoring. In high concentrations and under certain
environmental conditions, nutrients can lead to algal
growth. In extreme situations, nutrients can cause
abundant growth of cyanobacteria, which are responsible
for the production of cyanotoxins and other compounds that
can affect the taste and odor of drinking water supplies.
Potential sources of nutrients in aquatic systems include
animal waste, leaking septic systems, fertilizer run-off,
erosion, and atmospheric deposition.
Ammonia (NH3-N), nitrate (NO3-N), nitrite (NO2-N), and
ortho-phosphate (PO4) are dissolved forms of nitrogen and
phosphorus that are readily available for plant uptake. Both
Total Kjeldahl Nitrogen (TKN) and Total Phosphorus (TP)
serve as aggregate measures of potential nitrogen and
phosphorus availability to the system.
Total nitrogen (TN) is the sum of TKN and inorganic
nitrogen (NO3-N and NO2-N). TKN is a measure of
ammonia plus organic nitrogen and comprises the largest
fraction of TN, with inorganic nitrogen representing lesser
fraction. Likewise, TP is a measure of dissolved
phosphorus as well as phosphorus bound to sediments and
organic matter. For this report, the discussion of results
only pertains to values above the reporting limits currently
used by the FCWQL. Current reporting limits are 0.005
mg/L (5 μg/L) for PO4, 0.01 mg/L (10 μg/L) for ammonia
and TP, and 0.04 mg/L (40 μg/L) for nitrate and nitrite. In
the calculation of TN (TKN + NO3-N + NO2-N),
concentrations below their respective reporting limit were
reported as half the reporting limit (Helsel and Hirsch,
2002).
Caution should be taken when interpreting the observed
long-term trends for most nutrient water quality constituents
because of the uncertainty associated with values reported
below the reporting limit. In most cases, trend slope output
from the SMKT revealed zero rate of change for significant
trends, and therefore, corresponding trend results bar
graphs were not included in the presentation of results.
Instead, median values measured over the recent five-year
period were compared to the baseline median values.
Nitrogen
Total nitrogen appeared to increase at all monitoring sites
over the long-term period of record throughout the
Mainstem CLP watershed. Total nitrogen gradually
increased at high- to mid-elevation monitoring sites from
Joe Wright Creek to Mainstem CLP river above the South
Fork CLP river (PBR). TN significantly increased 9 μg L-1
per year at PJW over the long-term period, but this trend
did not appear to influence TN downstream at PBR. Step
trends in TN were observed at monitoring sites from the
South Fork CLP river downstream to PBD (Figure 4.8). A
notable increase in TN was also measured in the North Fork
CLP watershed at NDC. No trends were observed for TKN.
Nitrate followed a similar pattern to that of total nitrogen
over the long-term period of record, but there was
uncertainty in the observed long-term trend because
Figure 4.8 – Smoothed time-series plot for total nitrogen
on the Mainstem (top) and corresponding trend results with
24 UPPER CACHE LA POUDRE WATERSHED COLLABORATIVE WATER QUALITY MONITORING PROGRAM
Figure 4.9 – Median nitrate and ammonia concentrations over the recent five-year period compared to baseline concentrations on
the Mainstem and North Fork CLP rivers. The red line indicates the City of Fort Collins Water Quality Laboratory’s reporting limit.
+s = significantly increasing step trend and + = significant increasing long-term trend
100
50
0
Baseline
2017
2016
2015
2014
2013
100
50
0
Baseline
2017
2016
2015
2014
2013
100
50
0
03JWC
NITRATE as N, ug/L
04PJW
06PBR 08PSF
09PNF 10PBD
100
50
0
Baseline
2017
2016
2015
2014
2013
100
50
0
Baseline
2017
2016
2015
2014
2013
100
50
0
11NDC
NITRATE as N, ug/L
12NBH
13NRC 17NFL
18NFG
40
20
0
Baseline
UPPER CACHE LA POUDRE RIVER COLLABORATIVE WATER QUALITY MONITORING PROGRAM 25
concentrations were below the reporting limit at most sites
over the baseline period. Significant step trends were
observed at monitoring sites from the South Fork CLP river
downstream to PBD in the years following wildfire. In
contrast, there were no step trends detected at higher
elevation monitoring sites in the Mainstem CLP watershed
providing further evidence of wildfire related impacts on
water quality (Figure 4.9).
Nitrate concentrations in the years following the wildfire
were 1 – 2 times greater than baseline conditions, but still
relatively low (Figure 4.9). Median nitrate concentrations
were trending down to baseline conditions over the recent
five-year period suggesting watershed recovery (Figure
4.9). No long-term trends were detected in nitrate on the
North Fork CLP watershed, but nitrate concentrations
below Halligan and Seaman Reservoir were slightly higher
over the recent five-year period compared to baseline
conditions (Figure 4.9).
A significantly increasing trend was detected in ammonia at
most monitoring sites throughout both the Mainstem and
North Fork CLP watersheds. Higher concentrations over
the recent five-year period were responsible for the
observed long-term trend. Ammonia concentrations
measured during the baseline period of record were
routinely below the laboratory’s reporting limit (20 μg/L) at
most sites, except below Halligan and Seaman Reservoirs
where concentrations are usually detected above the
reporting limit (Figure 4.9). In recent years, ammonia
concentrations throughout the Upper CLP watershed were
detected above the reporting limit more often and median
ammonia concentrations over the five-year period were
greater than baseline conditions, especially on the North
Fork CLP river where median concentrations were 1 – 3
times greater than baseline conditions (Figure 4.9). The
exact cause of elevated ammonia throughout the
watershed is unknown; however, atmospheric deposition
may be an attributable source.
Phosphorus
Site specific long-term trends were identified in total
phosphorus in both the Mainstem and North Fork CLP
watersheds. Significantly increasing trends in TP were
measured on Joe Wright Creek (CHR and JWC), the South
Fork CLP river and the Mainstem CLP river below the
confluence with the North Fork (PBD). TP concentrations
on Joe Wright Creek steadily increased over the long-term
period of record, whereas an abrupt increase in TP
100
50
0
2008 2013 2018
100
50
0
2008 2013 2018
100
50
0
11NDC
TOTAL PHOSPHORUS, ug/L
26 UPPER CACHE LA POUDRE WATERSHED COLLABORATIVE WATER QUALITY MONITORING PROGRAM
concentrations was observed at monitoring sites located
within the High Park wildfire burn scar (Figure 4.10).
Median TP concentrations measured over the recent five-
year period were elevated compared to baseline conditions.
The highest concentrations were measured in the year
immediately following the wildfire at PNF and PBD, but
concentrations fell in subsequent years. Median TP
concentrations at PNF were below baseline conditions in
2017, implying watershed recovery and a return to pre-fire
conditions. TP concentrations remained elevated at PBD,
which may be attributed to significantly increasing TP
concentrations on the North Fork CLP river below Seaman
Reservoir at NFG. A significantly increasing trend was also
measured on the North Fork CLP river above Halligan
Reservoir at NDC (Figure 4.10). Median TP
concentrations steadily increased over the recent five-year
period with the highest median concentration measured in
2017.
Step trends were detected in ortho-phosphate at most
monitoring sites throughout the Mainstem and North CLP
watersheds. Median ortho-phosphate concentrations over
the current five-year period were measured slightly above
the laboratory reporting limit, while baseline conditions
were generally below the reporting limit (Figure 4.11).
Ortho-phosphate concentrations were slightly higher than
the reporting limit from JWC downstream to PSF in 2015
and 2016, which may be attributable to flooding in 2013. In
general, ortho-phosphate steadily increased from 2013 to
2015 and then slowly returned to baseline conditions by
2017. This short-term watershed wide trend in ortho-
phosphate provides further evidence of water quality
impacts associated with the 2013 flood event.
Figure 4.11 – Median ortho-phosphate over the recent five-year period compared to baseline concentrations on the Mainstem and
North Fork CLP rivers. The red line indicates the City of Fort Collins Water Quality Laboratory’s reporting limit. +s = significant
increasing step trend and + = significantly increasing long-term trend
30
15
0
Baseline
2017
2016
2015
2014
2013
30
15
0
Baseline
2017
2016
2015
2014
2013
30
15
0
03JWC
ORTHO-PHOSPHATE, ug/L
04PJW
UPPER CACHE LA POUDRE RIVER COLLABORATIVE WATER QUALITY MONITORING PROGRAM 27
4.5 MICROORGANISMS
Total Coliform and E. coli
Coliforms are types of bacteria found naturally in the
environment in plant and soil material, but can also found
in the digestive tract of animals, including humans.
Disease causing bacteria or pathogens can be introduced
to the raw drinking water supply from fecal contamination.
The Upper CLP Collaborative Monitoring Program tests its
source water supply for the presence of bacterial
contamination by measuring the total amount of coliforms,
an indicator organism for the presence of pathogenic
bacteria. In addition, Escherichia coli (E. coli) is measured
and used as an indicator of human or animal fecal waste
pollution since the source of origin is more specific than
total coliforms. Total coliform counts are greater than E.
coli counts because total coliform includes all types and
sources of coliform bacteria.
Site specific trends were identified in total coliforms and E.
coli in the Upper CLP watershed. Median total coliforms
were greater over the current five-year period compared to
baseline conditions at all sites (Figures 4.12). A step trend
was identified at PNF with significantly higher counts of total
coliforms over the current five-year period. Median total
coliform counts were 1.5 times higher than baseline
conditions (327 CFU/100 mL and 488 CFU/100 mL
measure for current and baseline, respectively). A similar
step trend was measured downstream at PBD, but
contributions from the North Fork may have diluted the
trend considering total coliforms significantly decreased on
North Fork CLP river at NFG over the long-term period of
record. The abrupt increase at monitoring sites on the
Mainstem CLP river is likely a result of increased erosion
and delivery of coliforms following the wildfire.
E. coli significantly increased 0.50 CFU/100 mL per year at
PBR over the long-term monitoring period, which is likely
caused by a steadier increase in recent years. This trend
may indicate aging and leaking septic systems located near
the river in the Town of Rustic. No other trends were
identified in E. coli in the Mainstem CLP watershed or at
NFG on the North Fork CLP river, although cell counts were
higher over the current five-year period compared to
baseline conditions (Figure 4.12).
Figure 4.12 – Median total coliforms (top) and E. coli
(bottom) over the recent five-year period compared to
baseline concentrations on the Mainstem and North Fork
CLP rivers. + = significantly increasing trend and - =
significantly decreasing trend.
20
10
0
Baseline
2017
2016
2015
2014
2013
20
10
0
UPPER CACHE LA POUDRE RIVER COLLABORATIVE WATER QUALITY MONITORING PROGRAM 29
5.0 SUMMARY &
IMPLICATIONS
5.1 WATERSHED IMPACTS & ISSUES
OF CONCERN
Over the past ten years (2008 – 2017) the Upper CLP
watershed has experienced periods of wet and dry water
years influencing both streamflow and water quality
conditions in the CLP watershed. It is projected with current
climate models that the frequency and timing of wet and dry
years will be more unpredictable in the future. The most
serious consequences of climate change on Colorado
watersheds include: changes in precipitation and
streamflow patterns, increasing severity and frequency of
droughts and wildfires, and increasing frequency and
intensity of forest insects and disease.
Over the past two decades several forest insects and
diseases have impacted Colorado’s forests. The mountain
pine beetle (MPB), a native bark beetle that infests all pine
species, impacted over 3 million acres of Colorado’s forest
over the past two decades. The spruce beetle has
destroyed 1.78 million acres since 1996 and has been
Colorado’s most common forest pest insect over the past
six. In 2017, the Colorado State Forest Service identified
significant infestations in Larimer County and noted the
potential for expanding outbreaks in susceptible
Engelmann spruce forests in the northern portion of the
state suggesting the potential for future infestations and
tree mortality in the Upper CLP watershed.
Exceptionally hot and dry conditions in 2012 lead to
extreme drought and two major wildfires causing extensive
disturbance to mid- and low- elevations of the Mainstem
CLP watershed and the area surrounding Seaman
Reservoir on the North Fork CLP river. Following the
wildfires, high intensity rainfall over the burn scar caused
severe flooding, erosion, and debris flows on the Mainstem
CLP river, often impacting water quality and water
treatment with little or no warning for WTP staff. The years
following the fires brought mostly average or above
average snowfall and precipitation to the watershed, which
has aided in watershed recovery; however, impacts to
water quality persist five years after these events.
In the year following the fire, the Upper CLP watershed
experienced a long-duration, high intensity rainfall event,
which caused severe flooding in streams and rivers
throughout the watershed. Flood peaks were several
orders of magnitude greater than expected baseflows
during that time of year, which may have lessened the
impacts to water quality following the wildfires by scouring
the river channel of ash and sediment deposits from
previous debris flow events; however, changes in water
quality in recent years may be attributable to the flood
disturbance caused by elevated baseflows and erosion.
The watershed response to atmospheric deposition is less
clear. The reduction in sulfur dioxide emissions has
lessened the amount of sulfuric acid in the atmosphere and
lead to declines in precipitation acidity and acidic deposition
into Colorado’s watersheds. Nitrogen deposition is more of
a concern as increasing trends in ammonium have been
observed in Colorado (Figure 2.4). It is expected that these
30 UPPER CACHE LA POUDRE WATERSHED COLLABORATIVE WATER QUALITY MONITORING PROGRAM
streamflow increased 9 cfs per year. No trends were
observed in the magnitude or timing of peak streamflow.
5.3 TRENDS IN WATER QUALITY
Water quality data collected throughout the Upper CLP
watershed were analyzed for long-term trends to determine
if concentrations of water quality parameters that have
historically had the most impact on treatment at the three
treatment plants have increased, decreased or stayed the
same over the ten-year period of record from 2008 to 2017.
Trend analyses were performed on all monitoring sites
throughout the Upper CLP watershed for the following
water quality parameters:
x Physical Parameters
x General Parameters
x Total Organic Carbon
x Nutrients
x Microorganisms
Two types of trends were identified in the Upper CLP
watershed. Monotonic trends were identified as gradual,
continuous changes (increasing or decreasing) in the data
over time and step trends were recognized as an abrupt
shift (up or down) in the data at a certain point in time. In
general, step trends were measured for most water quality
parameters at monitoring sites from the South Fork CLP
river (PSF) downstream to the Mainstem CLP river below
the confluence with the North Fork (PBD). These trends
Water Quality
Parameter
MAINSTEM CLP WATERSHED NORTH FORK CLP WATERSHED
JWC PJW PBR PSF PNF PBD NDC NBH NRC NFL NFG
Temperature + +
pH + + + + + + + + + +
Specific Conductivity - +s + + - - -
Turbidity +s +s - -
Alkalinity + +s +s + +
Hardness - +s +s
Total Dissolved Solids + + + +s +s +s + +
Total Organic Carbon + + + + + + -
Nutrients + + + +s +s +s + + + + +
Microorganisms + + -
Table 5.1 – Summary of water quality trends detected throughout the Upper CLP watershed over the long-term period from 2008 to
2017. (+ = increasing trend; - = decreasing trend; and +s = increasing step trend)
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occurred in response to the dramatic landcover change in
the Mainstem CLP watershed caused by wildfire that
burned in 2012.
Trends were detected at varying scales. Both site-specific
and watershed-wide trends were detected in the Upper
CLP watershed. Site-specific trends capture impacts to a
specific site, while watershed-wide trends imply a large
disturbance that impacted the entire basin or large areas of
basin impacting multiple monitoring locations.
Table 5.1 summarizes significant trends detected
throughout the Upper CLP watershed over the long-term
period from 2008-2017.
5.4 IMPLICATIONS TO WATER
TREATMENT
Long-term trends in certain water quality parameters may
pose issues to water treatment processes in the future. It
is anticipated that water quality impacts caused by recent
wildfire and flooding will recover with time. Wildfire
impacted water quality parameters are trending toward
baseline conditions in recent years implying watershed
recovery. However, climate change projections for
Colorado point to a warmer climate and unpredictable
precipitation patterns that will likely increase the frequency
and severity of drought and wildfires, and other extreme-
weather events that can impact to water quality.
Water quality changes and trends on the Mainstem CLP
river at PNF and PBD have the most direct impact to water
treatment at the City of Fort Collins’, Soldier Canyon Water
Authority and City of Greeley water treatment plants. The
following bullets summarize water quality trends detected
at PNF and PBR and implications to water treatment:
x Alkalinity and hardness were 1.5 – 2 times greater
over the recent five-year period compared to
baseline conditions. Elevated levels over this time
were caused by post-fire erosion and flood effects.
More alkaline water influences water pH and may
affect the taste of drinking water. Despite elevated
concentrations in recent years, alkalinity remains
relatively low in CLP raw water. Because of
seasonal influences on alkalinity levels in CLP raw
water, blending and chemical additions will
continue to be the best practice to meet drinking
water treatment goals.
x pH increased 0.07 units per year over the past
decade at PNF and PBD indicating that CLP raw
water is becoming more alkaline. Increasing CLP
raw water pH may affect the taste of drinking water
requiring additional blending with an alternate raw
water source or chemical additions to adjust pH
levels to meet drinking water treatment goals. pH
increased throughout the Upper CLP watershed
indicating a watershed wide change potentially
attributable to the watershed’s response to
declining precipitation acidity over the past two
decades. Elevated carbonates associated with
post-fire erosion and flooding may be elevating the
alkalinity at PNF and PBD.
x Total dissolved solids increased abruptly at PNF
and PBD following wildfire. Concentrations were
32 UPPER CACHE LA POUDRE WATERSHED COLLABORATIVE WATER QUALITY MONITORING PROGRAM
indicating watershed recovery and a return to pre-
fire baseline conditions.
x Total coliforms were greater over the recent five-
year period compared to baseline conditions at
PNF. Median total coliform counts were 1.5 times
higher than baseline conditions. A similar trend
was observed at PBD, but contributions from the
North Fork may have lessened the trend. The
abrupt increase at monitoring sites on the
Mainstem CLP river is likely a result of increased
erosion and delivery of coliforms following the
wildfire.
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6.0 DATA QUALITY
ASSURANCE AND
CONTROL
The Upper CLP watershed collaborative monitoring
program assures comparability and validity of data by
complying with monitoring methods and implementing
quality assurance and quality control (QAQC) measures.
QAQC measures are good practice in environmental
monitoring and can be used to determine potential error in
data due to contamination of water samples, sampling
error, equipment contamination, and/or laboratory error.
The Upper CLP monitoring sites are representative of the
goals and objectives outline previously and demonstrate
the true character of the watershed at the time of sampling.
The following summarizes QAQC data collected over the
2017 monitoring season. Refer to Upper CLP annual
reports for QAQC summaries for subsequent years (2013-
2016).
6.1 FIELD QUALITY CONTROL
In 2017, field duplicates were collected during each
Mainstem CLP monitoring event. Field duplicates (11
duplicates in total) were obtained at PNF during each
monitoring event to determine precision of data, while field
blanks (22 blanks in total) were collected at different
monitoring locations on both the Mainstem and North Fork,
to identify potential for sample contamination. The field
data quality sampling schedule is outlined in the 2017
annual sampling plan (Attachment 4). QAQC samples and
accuracy of field equipment is reviewed by Source
Watershed Program staff.
Field Duplicates
In 2017, twelve percent (33 out of 183) of the environmental
samples collected were QAQC samples. Precision is a
measure of the deviation from the true value. For most
constituents, duplicate determinations should agree within
a relative percent difference of 10%. Duplicate samples
that differ greater than 10% were flagged for further quality
assurance and control measures. Blank samples should
not contain analytes above the reporting limit. The results
of the field quality assurance and control sampling indicate
that precision and accuracy were acceptable.
Table 5 outlines relative percent difference statistics for
duplicate samples collected in 2017 and illustrates that
UCLP water quality data are of high precision. All duplicate
samples were within 10% agreement at the 50th percentile,
except for total phosphorus. Ammonia, orthophosphate,
total coliforms, TDS, TKN and total phosphorus were
slightly outside of the 10% agreement at the 75th percentile,
Field Blanks
Eighty-seven percent of field blank samples reported below
the constituent’s respective reporting limits in 2017. The
13% of field blank samples that were detected above the
reporting limits included Ni, NH3-N, turbidity, and TDS
Constituent
Range in
QAQC sample
concentration
Reporting
Limit
34 UPPER CACHE LA POUDRE WATERSHED COLLABORATIVE WATER QUALITY MONITORING PROGRAM
(Table 6.2). Water quality constituents that exceeded their
respective reporting limit were similar to blank exceedances
reported in previous years.
Concentrations exceedances were reported only slightly
above the reporting limit for most samples and
concentrations were minimal compared to concentrations
of environmental samples. Potential causes of these
contaminants are listed below:
x Atmosphere/particulates in the air slightly
increasing Ni, ammonia, turbidity, and total
dissolved solids. It is recommended to cap
sample bottles between rinses and as quickly as
possible following the blank sample collection.
x Inadequate rinsing of sample bottles either in the
field or laboratory may have left residuals
increasing turbidity and total dissolved solids. It is
recommended that sample bottles be subject to a
final rinse with deionize water in the laboratory
prior to storage and triple rinsed in the field with
deionize water prior to blank sample collection.
x Ammonia contamination may be introduced by the
field sampler and/or laboratory staff accidentally
breathing on the sample. It is suggested to limit
the amount of time the sample is exposed to the
environment by immediately capping the sample
bottle following sample collection and/or sample
processing in the laboratory.
Instrument Accuracy
Accuracy is a measure of the degree of closeness a
measurement is to the true measurement. Equipment
calibrations were conducted prior to field monitoring
exhibitions using certified standards to assure the accuracy
of sensors on the multi-parameter water quality sonde.
6.2 LABORATORY QUALITY CONTROL
Upper CLP water quality samples analyzed by the Fort
Collins Water Quality Laboratory are reviewed by the
Quality Assurance Coordinator to ensure data are free of
sample contamination, analytical, and/or data entry errors.
The City of Fort Collins Water Quality Laboratory
implements analytical QAQC measures by conducting
laboratory blank, duplicate, replicate, and spiked samples.
The City of Fort Collins WQL conducts a majority of
analyses for the Source Water Quality Monitoring Program,
and is a U.S. EPA Certified Drinking Water Laboratory with
an established QA plan that is applied to all samples
received by the laboratory (Elmund et al, 2013). The
primary features of their QA protocol include:
x Precision: one duplicate sample is analyzed for
every 10 samples; relative deviation should be
less than 10%.
x Accuracy: one external QCS sample is analyzed
with each set of samples analyzed. Methods
may specify an acceptable recovery range. In
general, Standard Methods limits are ± 5% and
EPA methods are ± 10%.
x Recovery: one sample is spiked for every 10
samples; if there are different matrices, at least
one sample per matrix is spiked. Limits for most
methods are ± 15%. If one type of matrix spike
UPPER CACHE LA POUDRE RIVER COLLABORATIVE WATER QUALITY MONITORING PROGRAM 35
7.0 REFERENCES
Billica, Loftis and Moore, 2008. Design of a Collaborative
Water Quality Monitoring Program for the Upper Cache
la Poudre River. July 14, 2008.
Elmund, K., F. Schrupp, J. Cannon, S. Reed, 2013. Quality
Assurance Plan, Internal Environmental Services
Division Pollution Control & Water Quality Laboratories
Document. City of Fort Collins Water Quality Services
Division Technical Document, 36 pages.
Helsel, D.R. and R.M. Hirsch, 2002. Statistical Methods in
Water Resources, Techniques of Water-Resources
Investigations of the United States Geological Survey,
Book 4, Hydrological Analysis and Interpretation, United
States Geological Survey, 524 pages.
Hirsch, R.M., R.B. Alexander, and R.A. Smith.1991.
Selection of methods for the detection and estimation of
trends in water quality. Water Resour. Res. 27:803-813.
Lettenmaier. D.P. 1976. Detection of trends in water
quality data from records with dependent observations.
Water Resour. Res. 12:1037-1046.
Oropeza, J., 2012. City of Fort Collins Utilities 2011 Annual
Report for the Upper Cache la Poudre River
Collaborative Water Quality Monitoring Program, Internal
Water Production Report, 75 pages plus appendices.
Oropeza, J. and J. Heath, 2013. City of Fort Collins Utilities
Five Year Summary Report (2008-2012) Upper Cache la
Poudre River Collaborative Water Quality Monitoring
Program, Internal Water Production Report, August 20,
2013, 85 pages plus appendices.
Oropeza, J. and J. Heath, 2014. City of Fort Collins Utilities
2013 Annual Report for the Upper Cache la Poudre River
Collaborative Water Quality Monitoring Program.
Internal Water Production Report, 69 pages plus
appendices.
Thas O., L. Van Vooren, and J.P. Ottoy. 1998.
Nonparametric test performance for trends in water
quality with sampling design applications. J. American
Water Resour. Assoc.34(2):347-357.
Intergovernmental Panel on Climate Change, 2007,
Climate change 2007—The physical science basis:
Contribution of Working Group I to the Fourth
Assessment Report of the Intergovernmental Panel on
Climate Change, Cambridge University Press, 1009 p.
Yochum, S.E., 2015. Colorado Front Range Flood of
2013: Peak Flows and Flood Frequencies. Proceedings
of the 3rd Joint Federal Interagency Conference on
Sedimentation and Hydrologic Modeling, April 19-23,
Reno, Nevada, USA.
Heath, J., 2015. Upper Cache la Poudre Watershed
Standard Operating Procedure. City of Fort Collins
Water Quality Services Division Technical Document,
29 pages.
Colorado State Forest Service, 2017. 2017 Report on the
Health of Colorado’s Forests: Meeting the Challenge of
Dead and At-risk Trees. Colorado Department of
Natural Resources Report, 28 pages
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ATTACHMENT 1
LAND USE COMPARISON OF THE NORTH FORK AND MAINSTEM CLP (AREAS
CALCULATED USING USGS SEAMLESS GIS DATA SETS)
Land Use Comparison
North Fork
(acres)
Main Stem
(acres)
North Fork Area
(%)
Main Stem
Area (%)
Developed land (commercial, industrial,
residential, urban, and utilities) 2,817 1,945 0.8 0.7
Agricultural use and grassland
(Cropland, pasture, other agriculture,
scrub and grasses)
183,719 54,765 52.3 18.3
Forest (forest and brush) 154,654 213,879 44.1 71.5
Natural lands (exposed rock, bare
ground, wetlands, tundra, lakes) 9,926 28,473 2.8 9.5
Total 351,116 299,062 100 100
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ATTACHMENT 2
UPPER CLP COLLABORATIVE WATER QUALITY MONITORING PROGRAM SAMPLING SITE
MAIN STEM Description Rationale GPS Coordinates
100CHR Chambers Lake Outflow Outflow from Chambers Lake N 40° 36.039
W 105° 50.203
090BMR Barnes Meadow Reservoir outflow High TOC and nutrients compared to CHR N 40° 36.039
W 105° 50.203
080JWC Joe Wright Creek at Aspen Glen
Campground
Joe Wright Creek above confluence with main
stem
N 40° 37.233
W 105° 49.098
070PJW Poudre at Hwy14 crossing (Big South
Trailhead) Above confluence Joe Wright Creek
N 40° 38.074
W 105° 48.421
060LRT Laramie River at Tunnel at Hwy 14
crossing Laramie River diversion water
N 40° 40.056
W 105° 48.067
050PBR Poudre below Rustic Midpoint between Laramie River Tunnel and
South Fork; impacts to river from Rustic
N 40° 41.967
W 105° 32.476
040SFM South Fork at bridge on Pingree Park Rd.
Discontinued in 2015
Only access point on South Fork; South Fork
water quality differs from main stem
N 40° 37.095
W 105° 31.535
041SFC South Fork above confluence with
Mainstem Capture 15% more watershed area than SFM
030PSF Poudre below confluence with South
Fork - Mile Marker 101 Below confluence with South Fork
N 40° 41.224
W 105° 26.895
020PNF Poudre above North Fork 1/2 mile
upstream from Old FC WTP#1
Represents water diverted at Munroe Tunnel
and at Old FC WTP #1
N 40° 42.087
W 105° 14.484
010PBD Poudre at Bellvue Diversion Greeley WTP Intake N 40° 39.882
W 105° 12.995
NORTH FORK
280NDC North Fork above Halligan Reservoir;
above confluence with Dale Creek Inflow to Halligan Reservoir
N 40° 53.852’
W 105° 22.556’
270NBH North Fork at USGS gage below Halligan
Reservoir Outflow from Halligan Reservoir
N 40° 52.654’
W 105° 20.314’
260NRC North Fork above Rabbit Creek Main stem North Fork above Rabbit Creek;
downstream of Phantom Canyon
N 40° 49.640
W 105° 16.776
250RCM Rabbit Creek Mouth
UPPER CACHE LA POUDRE RIVER COLLABORATIVE WATER QUALITY MONITORING PROGRAM 41
ATTACHMENT 3
2016 UPPER CLP MONITORING PARAMETER LIST
Rationale Notes
Field Parameters
Conductance Indicator of total dissolved solids. All sites with water quality
sonde.
Dissolved Oxygen Profile indicates stratification, importance for aquatic life and
chemical processes.
All sites with water quality
sonde.
Temperature Reflects seasonality; affects biological and chemical processes;
water quality standard.
All sites with water quality
sonde.
pH Measure of acidity. All sites with water quality
sonde.
General & Miscellaneous Parameters
Alkalinity Indicator of carbonate species concentrations; Acid neutralizing
capacity of water; treatment implications.
Discharge Necessary for flow dependent analysis and load estimation.
Measured during sampling at
NRC, RCM, SCM, PCM, PJW,
SFC when conditions allow
Geosmin Taste and odor compound Measured monthly at PBR
and PNF
Hardness Treatment implications. Hard water causes scaling and soft water is
considered corrosive.
Total Dissolved Solids
(TDS)
Indicator of overall water quality; includes both ionic and non-ionic
species.
Total Organic Carbon
(TOC)
Important parameter for water treatment; precursor of disinfection
byproducts.
Turbidity Indicator of suspended material; important for water treatment.
Nutrients
Nitrogen, Ammonia
Primary source of nitrogen to algae, indicator of pollution by
sewage, septic tanks, agriculture and atmospheric deposition; water
quality standard.
Nitrate
Primary source of nitrogen to algae; indicator of pollution by sewage,
septic tanks, agriculture, and atmospheric deposition; water quality
standard.
Nitrite Toxic inorganic nitrogen species; rarely encountered at significant
concentrations; water quality standard.
Total Kjeldahl
Nitrogen Sum of organic nitrogen and ammonia.
Ortho-Phosphorus
(Soluble Reactive
Phosphorus)
Form of phosphorous (dissolved PO4 -3) most available to algae;
indicator of pollution by sewage, septic tanks, agriculture and
atmospheric deposition.
Total Phosphorus
Includes dissolved and adsorbed, organic and inorganic forms of
phosphorus, indicator of pollution by sewage, septic tanks,
agriculture and atmospheric deposition.
42 UPPER CACHE LA POUDRE WATERSHED COLLABORATIVE WATER QUALITY MONITORING PROGRAM
Major Ions
Calcium Major ion. 6x/yr
Chloride Major ion. 6x/yr
Magnesium Major ion. 6x/yr
Potassium Major ion, minor importance as a nutrient. 6x/yr
Sodium Major ion. 6x/yr
Sulfate Major ion. 6x/yr
Microbiological Constituents
E. Coli Indicator of human or animal waste contamination; water quality
standard.
Only from Rustic downstream,
NFL, NFG, SER
Total Coliform Indicator of human or animal waste contamination. Only from Rustic downstream,
NFL, NFG, SER
Cryptosporidium Pathogen, indicator of human or animal waste contamination.
Monthly above and below
Halligan Reservoir, and below
Seaman Reservoir
Giardia Pathogen, Indicator of human or animal waste contamination.
Monthly above and below
Halligan Reservoir, and below
Seaman Res
Metals
Aluminum, total &
dissolved
Natural occurs in rocks and soil. Indicator of pollution from mining
activity at elevated levels; Aesthetic effects to drinking water Only PNF & NFG
Arsenic, total &
dissolved
Natural occurs in rocks and soil. Indicator of pollution from mining
activity at elevated levels; water quality standard. Only PNF & NFG
Cadmium, total &
dissolved
Natural occurs in rocks and soil. Indicator of pollution from mining
activity at elevated levels; water quality standard. Only PNF & NFG
Chromium, dissolved Natural occurs in rocks and soil. Water quality standard. Only PNF & NFG
Copper, dissolved Natural occurs in rocks and soil. Water quality standard. Only PNF & NFG
Iron, total & dissolved Natural occurs in rocks and soil. Affects aesthetic quality of treated
water. Only PNF & NFG
Lead, total &
dissolved
Natural occurs in rocks and soil. Indicator of pollution from mining
activity at elevated levels; water quality standard. Only PNF & NFG
Manganese, total &
dissolved
Natural occurs in rocks and soil. Aesthetic effects to drinking water;
water quality standard Only PNF & NFG
Nickel, dissolved Natural occurs in rocks and soil. Indicator of pollution from mining
activity at elevated levels; water quality standard. Only PNF & NFG
Silver, dissolved Natural occurs in rocks and soil. Indicator of pollution from mining
activity at elevated levels. Only PNF & NFG
Zinc, total & dissolved Natural occurs in rocks and soil. Indicator of pollution from mining
activity at elevated levels. Only PNF & NFG
Mercury, Low Level Accumulates in fish tissue even when present in very low
concentrations. Sample every 3 to 5 yrs.
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ATTACHMENT 4
UPPER CLP COLLABORATIVE WATER QUALITY MONITORING PROGRAM 2016 SAMPLING PLAN
2017 Sampling Dates
Apr 10 -11 Apr 24-25 May 8-9 May 22-23 Jun 5-6 Jun 20-21 Jul 10-11 Aug 14-15 Sep 11-12 Oct 16-17 Nov 13-14
Station
North Fork CLP
NDC F,G,P, F,G,I,B F,G,P F,G,I F,G,P F,G,I F,G,P F,G,I,P F,G,P F,G,I,P F,G,I,P
NBH F,G,P, F,G,I, F,G,P F,G,I F,G,P F,G,I F,G,P F,G,I,P F,G,P F,G,I,P F,G,I,P,B
NRC F,G,D F,G,I,D F,G,D F,G,I,D F,G,D F,G,I,D,B F,G,D F,G,I,D F,G,D F,G,I,D F,G,I,D
RCM G,D F,G,I,D F,G,D F,G,I,D F,G,D F,G,I,D ---------- ---------- ---------- ---------- ----------
SCM G,D F,G,I,D F,G,D F,G,I,D F,G,D F,G,I,D ---------- ---------- ---------- ---------- ----------
PCM G,D F,G,I,D F,G,D F,G,I,D F,G,D F,G,I,D ---------- ---------- ---------- ---------- ----------
NFL F,G F,G,I F,G F,G,I,B F,G F,G,I F,G, F,G,I F,G F,G,I F,G,I
NFG F,G,E,P F,G,I,E F,G,E,P F,G,I,M,E F,G,E,P F,G,I,E F,G,E,P F,G,I,E,P,B F,G,E,P F,G,I,M,P,E F,G,I,P,E
Mainstem CLP
CHR F,G F,G,I F,G F,G,I F,G F,G,I F,G F,G,I F,G F,G,I F,G,I
BMR2
F,G F,G,I F,G F,G,I F,G F,G,I F,G F,G,I F,G F,G,I F,G,I
JWC F,G,B F,G,I F,G F,G,I F,G F,G,I F,G F,G,I F,G F,G,I F,G,I
PJW F,G,D F,G,I,D F,G,D F,G,I,D F,G,D F,G,I,D F,G,D F,G,I,D F,G,D F,G,I,D,B F,G,I,D
LRT F,G F,G,I F,G F,G,I F,G F,G,I F,G F,G,I F,G F,G,I F,G,I
PBR F,G,E,T F,G,I,E F,G,E,T, B F,G,I,E F,G,E,T F,G,I,E F,G,E,T F,G,I,E,T F,G,E,T F,G,I,E,T F,G,I,E,T
SFC3
F,G,D F,G,I,D F,G,D F,G,I,D F,G,D,B F,G,I,D F,G,D F,G,I,D F,G,D F,G,I,D F,G,I,D
PSF F,G,E F,G,I,E F,G,E F,G,I,E F,G,E F,G,I,E F,G,E F,G,I,E F,G,E F,G,I,E F,G,I,E
PNF F,G,E,T,2 F,G,I,E,2 F,G,E,T,2 F,G,I,E,M,2 F,G,E,T,2 F,G,I,E,2 F,G,E,T,2 F,G,I,E,T,2 F,G,E,T,2 F,G,I,E,M,T,2 F,G,I,E,T,2
PBD F,G,E F,G,I,E F,G,E F,G,I,E F,G,E F,G,I,E F,G,E,B F,G,I,E F,G,E F,G,I,E F,G,I,E
1 Grab samples taken at two depths (Top & Bottom); depth profiles at 1-m intervals.
2 Call River Commissioner to find out if water is flowing. If not flowing, skip sample.
3 SFC = South Fork above Confluence w/ Mainstem, new site in 2014 to capture fire impacts.
Blanks analyzed for NH3, NO3, TOC, TDS, NTU and Cl-
2 = Duplicate, A = Algae (Lugol’s); B=Blank, C = Chlorophyll (500 mL sample); D =
Flow; F = Field data (Temp, pH, conductance streams + Secchi, DO for lake);
G = 1 liter sample for general, nutrients, TOC; E = E. coli, coliform (500 mL sterile
bottle); I = Major ions; M = Metals; P = Giardia/Cryptosporidium; T=Geosmin
2.6
Packet Pg. 128
Attachment: 2017 Five Year Upper Poudre River Water Quality Report (8063 : Water Resources,
UPPER CACHE LA POUDRE RIVER COLLABORATIVE WATER QUALITY MONITORING PROGRAM 45
ATTACHMENT 5
ANALYTICAL METHODS, REPORTING LIMITS, SAMPLE PRESERVATION,
AND HOLDING TIMES
Parameter Method Reporting Preser- Holding
Limit vation Time
Micro- Total Coliform, E.coli - QT SM 9223 B 0 cool, 4C 6 hrs
biological
Giardia & Cryptosporidium
(CH Diagnostics) EPA 1623 0 cool, 4C 4 days
Algae I.D. (Phyto Finders) SM 10200E.3,
SM 10200F.2c1
Lugol's Solution,
cool, 4C 12 mo
General & Alkalinity, as CaCO3 SM 2320 B 2 mg/L cool, 4C 14 days
Misc. Chlorophyll a SM10200H modified 0.6 ug/L cool, 4C 48 hrs
Hardness, as CaCO3 SM 2340 C 2 mg/L none 28 days
Specific Conductance SM 2510 B cool, 4C 28 days
Total Dissolved Solids SM 2540 C 10 mg/L cool, 4C 7 days
Turbidity (NTU) SM2130B,EPA180.1 0.01 units cool, 4C 48 hrs
Nutrients Ammonia - N Lachat 10-107-06-2C 0.01 mg/L H2SO4 28 days
Nitrate EPA 300 (IC) 0.04 mg/L cool, 4C (eda) 48 hrs
Nitrite EPA 300 (IC) 0.04 mg/L cool, 4C (eda) 48 hrs
Total Kjeldahl Nitrogen EPA 351.2 0.1 mg/L H2SO4 pH<2 28 days
Phosphorus, Total SM 4500-P B5,F 0.01 mg/L H2SO4 pH<2 28 days
Phosphorus, Ortho SM 4500-P B1,F 0.005 mg/L filter, cool 4C 48 hrs
Major Ions Calcium EPA 200.8 0.05 mg/L HNO3 pH <2 6 mos
Chloride EPA 300 (IC) 1.0 mg/L none (eda) 28 days
Magnesium, flame EPA 200.8 0.2 mg/L HNO3 pH <2 6 mos
Potassium EPA 200.8 0.2 mg/L HNO3 pH <2 6 mos
Sodium, flame EPA 200.8 0.4 mg/L HNO3 pH <2 6 mos
Sulfate EPA 300 (IC) 5.0 mg/L cool, 4C (eda) 28 days
Metals Cadmium EPA 200.8 0.1 ug/L HNO3 pH <2 6 mos
Chromium EPA 200.8 0.5 ug/L HNO3 pH <2 6 mos
Copper EPA 200.8 3 ug/L HNO3 pH <2 6 mos
Iron, (total & dissolved) EPA 200.8 10 ug/L HNO3 pH <2 6 mos
Lead EPA 200.8 1 ug/L HNO3 pH <2 6 mos
Nickel EPA 200.8 2 ug/L HNO3 pH <2 6 mos
Silver EPA 200.8 0.5 ug/L HNO3 pH <2 6 mos
Zinc EPA 200.8 50 ug/L HNO3 pH <2 6 mos
TOC TOC SM 5310 C 0.5 mg/L H3PO4pH <2 28 days
Analysis conducted by City of Fort Collins Water Quality Lab (FCWQL), unless otherwise noted.
Reporting Limit = lowest reportable number based on the lowest calibration standard routinely used.
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Packet Pg. 129
Attachment: 2017 Five Year Upper Poudre River Water Quality Report (8063 : Water Resources, Watershed, and Water Quality Protection
A River Health Report Card
STATE POUDRE of the
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Packet Pg. 130
Attachment: Poudre River Health Report Card (8063 : Water Resources, Watershed, and Water Quality Protection Overview)
The purpose of the River Health Report Card is to provide a
description of the current health of the Poudre River from
approximately Gateway Natural Area to I-25. This Report Card
provides the City of Fort Collins with a new tool to benchmark
progress towards its vision of sustaining a healthy and resilient
Cache la Poudre River.
The Cache la Poudre River (Poudre) is a complex natural system
that has been altered by nearly two centuries of human use. This
has resulted in dramatic changes to water quantity and quality,
the physical structure of the river, floodplain, forests, and wildlife
communities associated with it. The human footprint continues
to expand, placing additional pressure (or stresses) on the river
ecosystem and the natural processes that sustain it.
OVERALL GRADE
For the study area the Poudre River received an overall grade
of C. This grade indicates that even though the Poudre has
been altered and degraded by a suite of local and system wide
stresses that impair its health, it continues to support basic
elements of a functioning river ecosystem.
APPROACH
While the Poudre flows 126 miles from its headwaters to its
confluence with the South Platte near Greeley this study
focuses on a 24-mile reach from the lower canyon through
Fort Collins. Six key indicator groups are informed by metrics,
the measurable elements of the system. Metrics grades are
developed by collecting and incorporating many types of data
and then translated into an A-F grading system.
COVERALL
GRADE
A River Health Report Card
SIX KEY INDICATORS GROUPS
were used to evaluate river health.
FLOWS
snowmelt brings high flows in spring and early summer. These high
flows refresh the riverbed for fish, scour away algae, and provide
water to riverside vegetation. Base flows are low flows that occur
throughout the rest of the year and sustain basic needs for life in
the river. Understanding fluctuation of flows (how quickly flow
volumes change over short time periods) is important as this can
create unnatural and challenging conditions for fish and insects.
SEDIMENT
Sediment includes soil, sand, and rock that are washed from
watershed slopes and the riverbanks into and down the river. A
natural component of all rivers, too much or too little can cause
imbalances in the river’s physical processes. An imbalance
the capacity of the river channel to convey large floods.
RIVER CHANNEL
The shape of the river’s winding path, its width and depth,
and the presence of finer in-stream habitats across faster and
slower moving waters influence this indicator group. The river’s
response, or resilience, to natural disturbances (such as floods or
drought) is closely linked to the condition of its physical setting.
WATER QUALITY
This is the chemical ability of water to support life,
including the plants and animals that live in and depend
on it including humans. Dissolved oxygen and temperature
are critical factors controlling which types of organisms
can live there. While nutrients are necessary to support
aquatic life, excessive levels can degrade water quality and
cause algal blooms, decreased clarity, and bad odor.
HORSETOOTH
RESERVOIR
SEAMAN
RESERVOIR
MUNROE
DIVERSION
CANYON
MOUTH
OVERLAND
TRAIL
TIMBERLINE
ROAD
INTERSTATE
25
Fort Collins
Canyon ZONE
Rural ZONE
Urban ZONE
Plains ZONE
TIMNATH
LORY STATE
PARK
SEDIMENT AND
RIVER CHANNEL
The river channel has seen drastic changes over
the past two centuries causing widespread
fundamental alterations to the ecosystem. The
river used to meander across the floodplain.
Forcing it into a single, permanent path has
disrupted various processes dependent on natural
river movement including the regeneration of
riparian forests, the movement and balance of
sediment, the river’s resilience to large floods, and
other events like wildfires in the upper watershed.
However, with today’s land uses, there is a
need to protect infrastructure in the floodplain.
Understanding this new physical dynamic and its
relationship with extreme flow events is central
to our success in managing for river health.
RIPARIAN CORRIDOR
The riparian corridor has experienced a system-
wide disconnect between the river and its
floodplain. In many places riverside forests form
only a narrow band that hugs the river banks
(%)%0%*#ˏ+2!.((ˏ.%,.%*ˏ$!(0$. However, where
the riparian corridor is connected to the river
there are pockets of healthy forests including a
mosaic of diverse habitats, which are ideal for
supporting wildlife. Restoring the river-
floodplain connection and active management of
aggressive non-native trees is making a positive
difference across City-owned floodplain
properties.
FLOWS
The Poudre is characterized by major changes
in flow volumes and timing. Reductions have
significantly altered peak and base flows, the
effects which are exacerbated the further one
travels downstream. Diversions also cause
unnatural fluctuations in flow volume, which
WHAT’S NEXT?
A “B” grade for river health is
desired to fulfill the City’s vision
for a healthy and resilient river.
This holistic and science-based
river assessment can help the City
evaluate operational, management,
and policy options for preserving
or enhancing the river’s health.
This assessment can also serve
as a benchmark for monitoring
river health and changes in the
future. Broader communication
and engagement of diverse Poudre
River stakeholders can strengthen
our impact to manage for a healthy
river now and in the future.
YOU CAN HELP
Direct your downspout to water some of your landscape with rain
instead of treated water. Use water-efficient fixtures and eliminate
water waste like leaky toilets or damaged irrigation equipment.
Conserves water, reduces overall water demand
from streams and rivers.
Clean up wastes around your home and pollutants like lawn
chemicals, pet waste, trash and automotive fluids so they don’t
wash into the storm drain when it rains.
Helps protect river water quality by preventing
pollutants in urban stormwater runoff.
Abide by regulations, wildlife and restoration closures,
and stay on trails to reduce erosion along banks.
Supports health of wildlife and vegetation.
Buy fishing license or Habitat Stamp from Colorado Parks and Wildlife. Supports Colorado Parks and Wildlife management
of fisheries.
Volunteer! Opportunities include river cleanups, water-related
boards and commissions, education and outreach.
Contact engage@fcgov.com.
Get out, recreate, participate in educational programs and enjoy
the beautiful wildlife, forests and sounds of flowing water.
Personal renewal, appreciation, reminds you why
river health is important to you and your community.
This report card represents a summary of findings.
For the full report and online mapping tool,
visit fcgov.com/poudrereportcard.
Auxiliary aids and services are available for persons with disabilities.
ACKNOWLEDGMENTS
This project was developed by a collaboration of
ecologists and resource managers from; City of Fort
Collins Natural Areas Department, City of Fort Collins
Utilities Watershed Program, Otak Inc., Ecometrics,
Johnson Environmental Consulting Inc., Timberline
Aquatics, Colorado Parks and Wildlife and AlpineEco.
2.7
Packet Pg. 133
Attachment: Poudre River Health Report Card (8063 : Water Resources, Watershed, and Water Quality Protection Overview)
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Attachment: PowerPoint Presentation (8063 : Water Resources, Watershed, and Water Quality Protection
likely affects critical habitat and reproductive
needs of fish and insects in the river.
WATER QUALITY
Water quality in the Poudre is quite good,
despite the presence of some stresses, and
is supported by the City’s commitment
to manage stormwater runoff and meet
regulatory requirements for treated
wastewater effluent. The City and others
closely track water quality, implementing quick
action if undesirable changes are detected.
AQUATIC LIFE
While non-native trout are thriving in Poudre’s
cooler waters (generally upstream from
College Avenue) the populations of native
fish are in sharp decline. These declines are
most likely due to fragmented habitat and
extended periods of extremely low base flows.
Other stresses likely influencing fishery health
include rapid fluctuation of flows, non-native
predatory fish and altered water temperatures.
A Suite of Diverse ssues
DRIVE POUDRE RIVER HEALTH
URBAN ZONE
Gravel pits and levees affect the river’s ability to access the
floodplain on the upstream end of the Urban zone, while
encroachment from roads and development through the City
have impacted the diversity and extent of the riverside forests
and habitats. Nevertheless, pockets of excellent riverside
forests exist (near Shields Street) where high spring flows
have access to the floodplain. The river once formed multiple
braided channels increasing the system’s capacity to mitigate
large floods, but now as a single, confined channel it has
reduced resilience to flooding. Diversion dams and the lack of
large wood in the channel negatively impact habitat for aquatic
insects and fish. While introduced non-native trout appear to
be doing well, a major concern is the local loss of native fish.
PLAINS ZONE
As the river flows through large areas of land managed as
conserved open lands river health improves slightly in the
Plains zone. Yet the legacy of land use and water diversions
continues to have a significant influence on river health.
Diminished peak flows and significantly impacted base flows
have created a smaller-than-natural river channel that is
frequently disconnected from its floodplain. Low numbers and
diversity of native fish are a major concern but fish passage
structures allow for better aquatic habitat connectivity.
A REFERENCE STANDARD self-sustaining with no management, thriving
HIGHLY FUNCTIONAL some stresses present, but remains resilient to large
B disturbances, may rely on limited management
FUNCTIONAL while basic functions are intact, stresses impair the system, and active
C management is needed to maintain long term viability; low resilience
D FUNCTIONALLY IMPAIRED severely altered, extensive management required to
sustain basic characteristics
F NON-FUNCTIONAL biologically unsuitable
GRADE KEY
Land Erosion
Habitat
Connectivity
Channel Erosion
Fish
(no data available)
Continuity
Aquatic Insects
Temperature
Fluctuation
Nutrients Base Flow
Dissolved Oxygen
Peak Flow
Floodplain
Connectivity
Structure
Resilience
River Form
Vegetation
Surrounding Area
River
Channel
River
Flows
Aquatic
Life
Riparian
Corridor
Water
Quality
Sediment
d
C
Land Erosion
Habitat
Connectivity
Trout Channel Erosion
Continuity
Aquatic Insects
Temperature
Fluctuation
Nutrients Base Flow
Dissolved Oxygen
Peak Flow
Floodplain
Connectivity
Structure
Resilience
River Form
Vegetation
Surrounding Area
River
Channel
River
Flows
Aquatic
Life
Riparian
Corridor
Water
Quality
Sediment
Land Erosion
Habitat
Connectivity
Fish Channel Erosion
Continuity
Aquatic Insects
Temperature
Fluctuation
Nutrients Base Flow
Dissolved Oxygen
Peak Flow
Floodplain
Connectivity
Structure
Resilience
River Form
Vegetation
Surrounding Area
River
Channel
River
Flows
Aquatic
Life
Riparian
Corridor
Water
Quality
Sediment
d
C
Land Erosion
Habitat
Connectivity
Channel Erosion
Native Fish
Aquatic Insects Continuity
Temperature
Fluctuation
Nutrients Base Flow
Peak Flow Dissolved Oxygen
Floodplain
Connectivity
Structure
Resilience
River Form
Vegetation
Surrounding Area
River
Channel
River
Flows
Aquatic
Life
Riparian
Corridor
Water
Quality
Sediment
id
C
Trout
ZONE HIGHLIGHTS
Flooded forest Johnny Darter
CANYON ZONE
Through the Canyon zone the river and riparian
corridor are confined by canyon walls. Highway
14 further limits the river’s space and ability to
mitigate large floods. Here the river supports
aquatic life, a narrow riparian forest,
and floodplain, but this zone marks the
beginning of an approximately 20-mile
reach of river that is heavily impacted by
multiple diversions which begin to reduce
flows and fragment aquatic habitat. The
upstream forested watershed provides
Fort Collins and surrounding communities
with a reliable and high quality drinking
water source, but in the lower Canyon
zone warming water temperatures emerge
as a potential concern for aquatic life.
RURAL ZONE
As the Poudre leaves the canyon the river
has its first opportunity to connect to a wider
floodplain, but impacts from levees, armored
banks, and channelization disconnect the
river from its floodplain. Native cottonwoods
dominate many riverside forests, however,
encroachment from agricultural lands affects the
health of the vegetation. Cooler waters released
from Horsetooth Reservoir lower water temperature
in this zone. The impact of multiple large water diversions
severely alters peak and base (low) flows.
AQUATIC LIFE
Introduced, non-native trout are prized for their recreational
values while small bodied native fish are valued as a central
element of a healthy Poudre River. Aquatic insects (insects
that live part of their life on the river bottom) are an essential
part of the river system and form the base of the food chain.
The upstream-downstream connectivity of river habitats
is a critically important component of this indicator.
RIPARIAN CORRIDOR
The interaction of land and water results in beautiful riverside
forests, wetlands, and grasslands. Also, a healthy river-floodplain
connection protects us in larger flood events because the river
can access its floodplain. Valued as critical habitat for the majority
of terrestrial wildlife, the riparian corridor supports river health
by slowing floodwaters, filtering pollutants, and forming habitats
for many animals closely tied to or dependent on the river itself.
2.7
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Tributary to North Fork; drainage area includes
agricultural/grazing lands; significant flows late
spring to early summer only
N 40° 48.615
W 105° 17.146
240SCM Stonewall Creek Mouth Tributary to North Fork; drains area east of Hwy
287
N 40° 48.458
W 105° 15.195
230PCM Lone Pine Creek Mouth
Tributary to North Fork; drainage area includes
Red Feather Lakes; significant flows late spring
to early summer only
N 40° 47.696
W 105° 17.231
220NFL North Fork at Livermore At USGS gage N 40° 47.269
W 105° 15.130
210SER Seaman Reservoir
Discontinued in 2015
Reservoir profiles; impacts to water quality from
nutrient loadings
N 40° 42.274
W 105° 14.210
200NFG North Fork below Seaman Reservoir At gage below Seaman Res; sample before flow
enters Poudre main stem
N 40° 42.143
W 105° 14.064
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fails and all other QC passes, those samples may
be flagged.
A complete description of laboratory personnel, equipment,
and analytical QA methods is outside of the scope of this
report and is not addressed in detail here. As part of the
City’s Environmental Services Division the WQL operates
under the guidance of a general QA plan (Elmund et al.,
2013).
Constituent Samples above
DL Total samples % exceedance Reporting Limit Max Exceedance
Ni (ug/L) 1 4 25% 1 1.11
NH3-N (ug/L) 8 22 36% 0.01 0.04
Turbidity (NTU) 16 22 73% 0.05 0.99
TDS (mg/L) 13 22 59% 10 23
Table 6.2 – Blank samples detected above their respective detection limit from 2013 to 2017.
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Absolute
Mean
Difference
Relative Percent Difference (%)
Percentile
min max 25th 50th 75th
Alkalinity (mg/L) 31.6 32.2 2 0.44 0.2 0.4 1.4
Hardness (mg/L) 34.0 34.3 5 0.3 0.2 0.5 0.7
Ammonia (ug/L) 18.2 26.3 10 3.1 5.5 9.6 16.2
Turbidity (NTU) 8.64 9.06 0.05 0.18 0.7 2.5 3.6
ortho-Phosphate (ug/L) 6 36 5 4 5.8 7.3 21.7
E. coli (cells/mL) 0 727 - 19 - - -
T. coli (cells/mL) 79 1046 - 137 5.7 7.5 15.0
TDS (mg/L) 85 97 10 11 5.8 7.9 12.6
TKN (ug/L) 475 511 100 54 3.2 7.1 16.2
TOC (mg/L) 9.57 9.62 0.5 0.1 0.7 0.8 1.0
Total P (ug/L) 44.2 60.3 10 7.0 4.6 12.1 23.6
Table 6.1 – Data quality assurance statistics calculated for duplicate samples collected at PNF monitoring location in 2017.
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20 mg/L (median) greater over the recent five-year
period compared to pre-fire baseline conditions,
but remain very low compared to finished drinking
water levels throughout the country. Elevated
TDS concentrations in CLP raw water do not pose
a health risk, but high concentrations indicate
elevated levels of minerals, salts, metals, cations
or anions. High levels of dissolved solids in
finished water can cause water quality concerns
including corrosion, scale formation or taste
issues if not addressed through treatment.
x Total organic carbon gradually increased 0.10
mg/L per year at PNF and 0.08 mg/L per year at
PBD over the past decade. Higher TOC levels in
CLP raw water pose concern due to the potential
for higher residual TOC (post-filtration) and
increased disinfection by-products (DBPs)
formation. Increasing TOC in the CLP raw water
supply may require additional blending with other
raw water sources or increased coagulant for
efficient TOC removal. Additional treatment
implications for higher CLP raw water TOC may
include increased removal requirements as
concentrations more frequently exceed 4.0 mg/L.
x Elevated nutrients (nitrate and ortho-phosphate)
were observed at PNF and PBD in years following
the wildfire. Concentrations were still relatively
low, but even small increases in nutrient loads in
low nutrient environments can lead to algal growth
and potential taste and odor issues. Nutrient
concentrations over the recent five-year period
have steadily decreased at PNF and PBD
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trends will continue in the future because of projected
population growth and oil and gas development along the
Colorado Front Range.
5.2 TRENDS IN CLIMATE &
WATERSHED HYDROLOGY
Long-term climate records throughout the Rocky Mountains
have indicated that annual mean minimum air temperatures
increased 0.7oC per decade with stronger trends in the
Colorado Rocky Mountains. These trends are consistent
with global air temperature trends (Intergovernmental Panel
on Climate Change, 2007). Over the past decade, similar
trends were detected in air temperature at higher elevations
in the Upper CLP watershed. Monthly mean air
temperatures increased 0.24°F (0.13°C) per year. This
trend was driven by increasing minimum temperatures
during the winter season.
Precipitation trends were not detected over the long-term
period of record. However, the maximum amount of water
contained within the snowpack (peak snow water
equivalent; SWE) decreased 1.03 inches per year over the
past decade suggesting higher elevations of the Upper CLP
watershed may receive less snowfall in the future. In
addition, the peak SWE to precipitation ratio decreased
over the last decade implying that precipitation patterns
may be shifting in the Upper CLP watershed.
Streamflow significantly increased in the Upper CLP
watershed over the long-term period of record. Monthly
mean streamflow increased 13 cfs per year and winter
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Baseline
2017
2016
2015
2014
2013
20
10
0
06PBR
E. COLI, CFU/100 mL
08PSF
09PNF 10PBD
18NFG
2000
1000
0
Baseline
2017
2016
2015
2014
2013
2000
1000
0
Baseline
2017
2016
2015
2014
2013
2000
1000
0
06PBR
TOTAL COLIFORMS, CFU/100 mL
08PSF
09PNF 10PBD
18NFG
-
+
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06PBR 08PSF
09PNF 10PBD
30
15
0
Baseline
2017
2016
2015
2014
2013
30
15
0
Baseline
2017
2016
2015
2014
2013
30
15
0
11NDC
ORTHO-PHOSPHATE, ug/L
12NBH
13NRC 17NFL
18NFG
+s +s
+s 3
+s
+s
+s +s
+s
+s
+s
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Attachment: 2017 Five Year Upper Poudre River Water Quality Report (8063 : Water Resources, Watershed, and Water Quality Protection
12NBH
13NRC 17NFL
18NFG
Figure 4.10 – Smoothed time-series plot for total phosphorus on the Mainstem (left) and North Fork (right).
40
20
0
2008 2013 2018
40
20
0
2008 2013 2018
40
20
0
03JWC
TOTAL PHOSPHORUS, ug/L
04PJW
06PBR 08PSF
09PNF 10PBD
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Attachment: 2017 Five Year Upper Poudre River Water Quality Report (8063 : Water Resources, Watershed, and Water Quality Protection
2017
2016
2015
2014
2013
40
20
0
Baseline
2017
2016
2015
2014
2013
40
20
0
03JWC
AMMONIA as N, ug/L
04PJW
06PBR 08PSF
09PNF 10PBD
40
20
0
Baseline
2017
2016
2015
2014
2013
40
20
0
Baseline
2017
2016
2015
2014
2013
40
20
0
11NDC
AMMONIA as N, ug/L
12NBH
13NRC 17NFL
18NFG
+s +s + +
+
+ +
+s 1
+
+ 4
+
+
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Attachment: 2017 Five Year Upper Poudre River Water Quality Report (8063 : Water Resources, Watershed, and Water Quality Protection
estimated trend slope (bottom).
480
360
240
2008 2013 2018
480
360
240
2008 2013 2018
480
360
240
03JWC
TOTAL NITROGEN, ug/L
04PJW
06PBR 08PSF
09PNF 10PBD
PBD
PNF
PSF
PBR
PJW
JWC
10
5
0
ug/L/yr
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drivers of increasing TOC in the Mainstem CLP watershed
include:
x Catchment characteristics
x Hydrology, climate and weather
x Declining atmospheric acid deposition
x Increasing In-stream algal production
x Increasing algal production in high alpine lakes
Table 4.2 – Total organic carbon removal requirements for
water treatment facilities based on source water alkalinity and
total organic carbon concentrations.
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80
11NDC
TOTAL DISSOLVED SOLIDS, mg/L
12NBH
13NRC 17NFL
18NFG
NFG
NFL
NRC
NBH
NDC
6
3
0
-3
-6
mg/L/yr
Figure 4.6 – Smoothed time-series plot for total dissolved solids on the Mainstem (top left) and North Fork (top right) CLP rivers and
corresponding trend results with estimated trend slope (bottom).
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Attachment: 2017 Five Year Upper Poudre River Water Quality Report (8063 : Water Resources, Watershed, and Water Quality Protection
NFL
NRC
NBH
NDC
3.0
1.5
0.0
-1.5
-3.0
mg/L/yr
PBD
PNF
PSF
PBR
PJW
JWC
0.6
0.4
0.2
0.0
-0.2
mg/L/yr
NFG
NFL
NRC
NBH
NDC
4
2
0
-2
-4
mg/L/yr
a)
b)
c)
d)
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Attachment: 2017 Five Year Upper Poudre River Water Quality Report (8063 : Water Resources, Watershed, and Water Quality Protection
PNF
PSF
PBR
PJW
JWC
1.0
0.5
0.0
-0.5
-1.0
uS/cm/yr
Figure 4.4 – Smoothed time-series plot for specific conductivity on the Mainstem (top left) and North Fork (top right) CLP rivers and
corresponding trend results with estimated trend slope (bottom).
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Attachment: 2017 Five Year Upper Poudre River Water Quality Report (8063 : Water Resources, Watershed, and Water Quality Protection
0.2
0.0
-0.2
-0.4
NTU/yr
8
4
0
2008 2013 2018
8
4
0
2008 2013 2018
8
4
0
03JWC
TURBIDITY, NTU
04PJW
06PBR 08PSF
09PNF 10PBD
Figure 4.3 – Smoothed time-series plot for turbidity on the Mainstem CLP river (left) and North Fork sites NDC and NFG (top
right). The corresponding trend results and estimated trend slope for all North Fork CLP rivers is located on the bottom right.
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Attachment: 2017 Five Year Upper Poudre River Water Quality Report (8063 : Water Resources, Watershed, and Water Quality Protection
PBR
PJW
JWC
0.08
0.06
0.04
0.02
0.00
pH UNITS/YR
NFG
NFL
NRC
NBH
NDC
0.08
0.06
0.04
0.02
0.00
pH UNITS/YR
Figure 4.2 – Smoothed time-series plot for pH on the Mainstem (top left) and North Fork (top right) CLP rivers and corresponding
trend results and estimated trend slope (bottom).
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were 1.5 – 3 times greater than baseline conditions.
Turbidity at these sites peaked in 2013 and gradually
decreased in the following years to near baseline
conditions. There were no trends in turbidity measured at
2008 2013 2018
16
14
12
10
2008 2013 2018
12NBH
TEMPERATURE, CELSIUS
18NFG
NFG
NFL
NRC
NBH
NDC
0.2
0.1
0.0
-0.1
-0.2
degrees Celsius/yr
Figure 4.1 – Smoothed time-series plot for water
temperature at NBH and NFG (top) and trend results for
North Fork CLP river sites.
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Attachment: 2017 Five Year Upper Poudre River Water Quality Report (8063 : Water Resources, Watershed, and Water Quality Protection
ZKLOHQRWDEOHWUHQGVZHUHLGHQWLILHGWRWKH
confidence level S).
Step trends were evaluated with the nonparametric Mann-
Whitney test. The Mann-Whitney test compares two
population medians and calculates the corresponding point
estimate and confidence interval. Step trends occurred in
response to the dramatic landcover change in the
Mainstem CLP watershed caused by wildfire that burned in
the summer of 2012. Based on this extreme event, the
long-term data set was divide into two separate periods of
record and population medians were compared using the
Mann-Whitney test at monitoring sites located within and
downstream of the wildfire burn scar ((SFC, PSF, PNF and
PBD). ‘Baseline conditions’ were defined as the period of
record from 2008 to 2012 and ‘current conditions’ were
defined as the period of record from 2013 to 2017.
Statistical significance was determined to the 95%
FRQILGHQFHLQWHUYDO S
ZKLOHQRWDEOHWUHQGVZHUH
LGHQWLILHGWRWKHFRQILGHQFHLQWHUYDO S
Selected Variables and Monitoring Sites
Trend analyses were performed on all monitoring sites
throughout the Upper CLP watershed for the water quality
parameters listed below:
x Physical Parameters
Temperature, pH, Conductivity, Turbidity
x General Parameters
Alkalinity, Hardness, Total Dissolved Solids
x Total Organic Carbon
x Nutrients
Nitrogen and Phosphorus
x Microorganisms
E. coli and Total Coliforms
These water quality parameters were selected because
they either have a direct impact on water treatment
processes or served as key indicators for other water
quality parameters that may influence water treatment.
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10
0
Total Precip
Peak SWE
PRECIPITATION, inches
Dec
Nov
Oct
Sep
Aug
Jul
Jun
May
Apr
Mar
Feb
Jan
2000
1500
1000
500
0
Baseline
Current
STREAMFLOW, cfs
Baseline Current Winter
Spring
Summer
Fall
5.4%
71.3%
20.1%
3.2% 9.0%
55.3%
32.2%
3.5%
1,181,912 acre-ft 1,728,250 acre-ft
Figure 3.4 – Monthly average streamflow for the baseline
period compared to the recent five-year period (top) and
seasonal distribution of streamflow for the baseline period
and current period (bottom).
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Attachment: 2017 Five Year Upper Poudre River Water Quality Report (8063 : Water Resources, Watershed, and Water Quality Protection
Feb
Jan
60
50
40
30
20
10
0
Baseline
Current
TEMPERATURE, degrees F
Figure 3.2 – Monthly mean precipitation totals for the
baseline period compared to the recent five-year period (top)
and seasonal distribution of precipitation for the baseline
period and current period (bottom).
Dec
Nov
Oct
Sep
Aug
Jul
Jun
May
Apr
Mar
Feb
Jan
7
6
5
4
3
2
1
0
Baseline
Current
PRECIPITATION, inches
Baseline Current Winter
Spring
Summer
Fall
24.2%
4.9%
33.0%
28.0%
25.2%
11.9%
33.8%
29.1%
227 inches 232 inches
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Attachment: 2017 Five Year Upper Poudre River Water Quality Report (8063 : Water Resources, Watershed, and Water Quality Protection
ZKLOH QRWDEOH WUHQGV ZHUe
identified to the 90% confidence level S
Hydrologic and Climatic Data Sources
The snow telemetry (SNOTEL) network, managed by the
Natural Resource Conservation Service, includes
approximately 600 automated monitoring sites located in
remote mountain watersheds throughout the United States
that measure snow water equivalent (SWE), accumulated
precipitation, and air temperature. Joe Wright SNOTEL,
located at an elevation of 10,120 feet, contains the longest
record of continuous measurements in the Cache la Poudre
Watershed dating back to 1978
(https://wcc.sc.egov.usda.gov/nwcc/site?sitenum=551).
The Cache la Poudre at Canyon Mouth near Fort Collins
(CLAFTCCO) streamflow monitoring station managed by
the Colorado Department of Water Resources
(http://www.dwr.state.co.us/) contains the longest record of
continuous streamflow in the Upper CLP watershed, dating
back to 1883. The streamflow monitoring station is located
at the Canyon Mouth and includes streamflow contributions
from both the Mainstem and North Fork watersheds.
3.1 AIR TEMPERATURE
The annual mean air temperature measured at Joe Wright
SNOTEL over the last five years was slightly warmer than
baseline conditions. The mean temperature over the
current five-year period was 35.6 degrees Fahrenheit (°F)
(2.0 degrees Celsius (°C)) compared to a mean baseline
temperature of 34.8°F (1.5°C) (Figure 3.1). Monthly mean
air temperatures in the Upper CLP watershed were slightly
warmer in most months over the recent five-year period
compared to baseline conditions. Five-year monthly mean
temperatures exceeded baseline monthly mean
temperature in all months except April, May, and August
(Figure 3.1).
Air temperature significantly increased at higher elevations
in the Upper CLP watershed over the long-term period of
record. A significant increase was detected in both the
average monthly mean and minimum air temperatures.
Average monthly mean temperatures increased at a rate of
0.24°F (0.13°C) per year, while average monthly minimum
temperatures increased at a slightly greater rate of 0.32°F
(0.18°C) per year (Table 3.1).
Seasonal trend analyses detected significantly increasing
average monthly mean and minimum air temperatures
during the winter season. Over the winter season, average
monthly mean temperatures increased at a rate of 0.32°F
per year, while average monthly minimum temperatures
increased at a rate of 0.37°F (0.21°C) per year (Table 3.1).
No additional seasonal trends were detected in average
monthly maximum air temperatures at the Joe Wright
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emitted into the air are deposited on land and water with
Raw Water Quality Finished Water Quality
Increased nutrients,
algae, cyanobacteria,
MIB, geosmin
Taste and odor, and
potential for cyanotoxins
Color and turbidity Color and turbidity
Increased microbial
contamination
Cryptosporidium and
giardia in treated water
Increased TOC DBPs (THMs and HAAs)
Low alkalinity Corroded pipes
Increased concentrations
of contaminants
Higher risk to public
health
Figure 2.2 – Percent normal rainfall over the U.S. West
between September 10 – 16, 2013. Part of Colorado received
more than 1000% of their normal rainfall (Source: National
Oceanic and Atmospheric Administration; www.climate.gov).
Table 2.3 – Potential raw and finished water quality impacts
related to flooding and extreme rainfall. Adopted from Water
Research Foundation Web Report #4324.
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much of the South Platte and Arkansas River Basins.
Intense rainfall was observed over a 7-day period from
September 9th to September 16th with some areas receiving
up to 18 inches of water (Figure 2.2). Several impacted
areas measured record rainfall amounts that were greater
than average annual perception totals.
Raw Water Quality Finished Water Quality
Increased nutrients,
algae, cyanobacteria,
MIB, geosmin
Taste and odor
Potential for cyanotoxins
Increased water
temperature
Increased water
temperatures in
distribution system
Color and turbidity Color and turbidity
Increased microbial
contamination
Cryptosporidium and
giardia in treated water
Iron and manganese Manganese, color
Increased TOC DBPs (THMs and HAAs)
Decreased DO
Increased hardness
Low alkalinity Corroded pipes
Increased concentrations
of contaminants
Higher risk to public
health
Table 2.1 – Potential raw and finished water quality impacts
related to drought. Adopted from Water Research Foundation
Web Report #4324.
Table 2.2 – Potential raw and finished water quality impacts
related to wildfire. Adopted from Water Research
Foundation Web Report #4324.
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summer and fall. The summer of 2012 (June-August) was
the warmest summer on record with statewide
temperatures greater than 4°F (2.2°C) warmer than the
long-term average temperature. Peak streamflow in June
of 2012 was less than 40% of the historical average
because of the low snowpack and hot, dry conditions
Figure 2.1 – Drought conditions in Colorado on July 3,
2012. Source: www.droughtmonitor.unl.edu
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downstream locations of the Upper CLP River near the City
of Fort Collins, SCWTA, and City of Greeley raw water
intake structures. In 2014, an additional monitoring location
was included on the South Fork (SFC) approximately 500
feet upstream of the confluence with the Mainstem Poudre
River. This monitoring location was added to the
monitoring network to capture the full extent of the South
Fork drainage following the 2012 High Park Fire. The South
Fork above Mainstem (SFM) site was discontinued in 2015
because analyses between SFC and SFM revealed similar
water quality conditions. The Seaman Reservoir (SER)
monitoring locations were also discontinued from the Upper
CLP monitoring program in 2015.
The current monitoring network consists of 18 monitoring
locations (Figure 1.1). A description and rationale for each
site is provided in Attachment 2.
1.3 SAMPLING PLAN AND
PARAMETERS
The sampling frequency for the Upper CLP monitoring
program was determined based on both statistical
performance and cost considerations. Parameters included
2.6
Packet Pg. 91
Attachment: 2017 Five Year Upper Poudre River Water Quality Report (8063 : Water Resources, Watershed, and Water Quality Protection
Climate & Hydrology Trends
Air temperature increased at higher elevations in the Upper
CLP watershed over the last decade. Precipitation volume
did not change, but the maximum amount of water
contained within the snowpack decreased over the past
decade suggesting higher elevations of the Upper CLP
watershed may receive less snowfall in the future. In
addition, snowpack and precipitation data imply that
precipitation patterns may be shifting in the upper CLP
watershed. No trends were measured in the magnitude or
timing of streamflow, but streamflow volume increased over
the long-term period of record specifically during the winter
months. This trend may be driven by the recent flood event
in 2013 and elevated baseflows for several years following
the flood.
Trends in Water Quality
Two types of trends were identified in the Upper CLP
watershed. In general, step trends (an abrupt shift in data)
were measured for most water quality parameters at
monitoring sites from the South Fork CLP river (PSF)
downstream to the Mainstem CLP river below the
confluence with the North Fork (PBD). These trends
occurred in response to the dramatic landcover change in
the Mainstem CLP watershed caused by wildfire that
burned in 2012. Monotonic trends, or gradual, continuous
changes (increasing or decreasing) in the data over time,
were measured in pH, total organic carbon, total dissolved
solids, and ammonia.
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Attachment: 2017 Five Year Upper Poudre River Water Quality Report (8063 : Water Resources, Watershed, and Water Quality Protection
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Attachment: Halligan Water Supply Project Agenda Item Summary (8063 : Water Resources, Watershed, and Water Quality Protection
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Attachment: Halligan Water Supply Project Agenda Item Summary (8063 : Water Resources, Watershed, and Water Quality Protection
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Attachment: Halligan Water Supply Project Agenda Item Summary (8063 : Water Resources, Watershed, and Water Quality Protection
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Packet Pg. 59
Attachment: Halligan Water Supply Project Agenda Item Summary (8063 : Water Resources, Watershed, and Water Quality Protection
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INTERSTATE 25
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N COUNTY ROAD 11
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INTERSTATE 25
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Water Districts
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ATTACHMENT 1 2.1
Packet Pg. 57
Attachment: Water Districts Map (8063 : Water Resources, Watershed, and Water Quality Protection Overview)
ground.
1.2
Packet Pg. 38
Attachment: Previous Council Priorities Dashboard, March 2019 (8030 : Council Priorities)
No further Council Action
planned
Other Info:
x Re-scoping is complete and
needed resource identified
x Currently implementing the
revised scope and have
initiated the project
1.2
Packet Pg. 37
Attachment: Previous Council Priorities Dashboard, March 2019 (8030 : Council Priorities)
Services/
Community &
Operation
Services
Next Council Action:
No regular meetings or work
sessions scheduled at this time
Other Info:
x Staff submitted an update
memo to Council on March
8, 2019 regarding current
City/;County/PSD
cooridination in the GMA;
projects under discussion
include: ped/bike
improvements along West
Vine Drive, and Trail
connections near Lincoln
Middle School.
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Attachment: Previous Council Priorities Dashboard, March 2019 (8030 : Council Priorities)
x Examine Fort Fund programs for
possible updates and revisions
Community
and
Operation
Services
Next Council Action:
No regular meetings or work
sessions scheduled at this time
Other Info:
x The Director of Cultural
Services, and the Director of
the Museum of Discovery,
met with the Mayor to
discuss the initiative and
believe that the FoCo
Creates Arts and Culture
Master Plan, as drafted,
addresses the initiative.
x Following editing and
refinement, the FoCo
Creates Arts and Culture
Draft Plan is being shared
with stakeholders and the
public in February and
March.
x An assessment of the Fort
Fund program is a proposed
action item in the Culture
Plan.
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Attachment: Previous Council Priorities Dashboard, March 2019 (8030 : Council Priorities)
Other Info:
x Second RFP for Home
Ownership product on
Kechter parcel closed late
February. Staff reviewing
responses.
x Grand Opening of Village on
Horsetooth on March 14
with 96 one-four bedroom
apartments. Leasing
ongoing.
x Work continues on acquiring
additional parcels
Ongoing
BEHAVIORAL
HEALTH / DETOX
FACILITY
Purpose: Partner with the County and
others to build capacity for behavioral
health services
Outcomes:
x Successful county ballot measure
for a facility
Identified ways to increase capacity in Fort
Collins in the interim
Sustainability
Services / City
Manager’s
Office
Next Council Action:
No regular meetings or work
sessions scheduled at this time
Other Info:
x Ballot measure passed in
November
x Council selected
Councilmember Stephens to
sit on the Policy Advisory
Committee
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Packet Pg. 34
Attachment: Previous Council Priorities Dashboard, March 2019 (8030 : Council Priorities)
Homes) to develop the
property. Staff has met
with representatives and
encouraged holding at
least 2 neighborhood
meetings as part of
community engagement
prior to submitting any
plans. The project is likely
to be residential with a mix
of housing types, solar, and
include a park.
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Attachment: Previous Council Priorities Dashboard, March 2019 (8030 : Council Priorities)
posted on FCPS website
x Presented Spanish policies
and plans to HRC in March
2019
NEIGHBORHOOD LIVABILITY & SOCIAL HEALTH
SHORT TERM
RENTAL REVIEW
Purpose: Review STR implementation and
consider potential code changes to address
known challenges and community feedback
Outcomes:
x Consider code changes
Continue to monitor implementation
City Manager’s
Office/
Planning,
Development,
and
Transportation
Next Council Action:
Work session on March 26, 2019
to discuss STRs in Multifamily
buildings.
Other Info:
Staff will present proposals at the
March 26 work session to
address building and fire code
issues in multifamily STRs.
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Attachment: Previous Council Priorities Dashboard, March 2019 (8030 : Council Priorities)
No regular meetings or work
sessions scheduled at this time
Other Info:
x Campus West Connections
substation continues to
host programs and
neighborhood events at the
facility
x This project continues to be
of value in bringing
agencies together to work
on neighborhood problems
around campus.
x Low walk-in traffic and
budget shortages have led
to a conversation about
reducing walk in hours.
x This facility continues to be
a catalyst for collaboration
and problem solving.
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Attachment: Previous Council Priorities Dashboard, March 2019 (8030 : Council Priorities)
x Support Transportation
Master Plan update in
2018/2019
x Finalized purchases of
electric municipal lawn and
garden equipment with 2018
funds
x Received 2019 RAQC
commercial lawn and garden
equipment grant.
x Ozone monitoring site
installed at the Gardens on
Spring Creek, and will be
accessible when new
Gardens areas are opened
in 2019.
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Attachment: Previous Council Priorities Dashboard, March 2019 (8030 : Council Priorities)
Council update memo planned
for April 2019.
Other Info:
x Continue outreach and
subsidized kit sales
x Received 2018-2019 state
funding
x Completed working group
meetings to evaluate
potential options to increase
testing and mitigation rates
x Presented working group
results to Air Quality
Advisory Board in February
2019
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Attachment: Previous Council Priorities Dashboard, March 2019 (8030 : Council Priorities)
scheduled at the June 25 Work
Session
Other Info:
x Fort Collins adopted a 100%
renewable electricity by
2030 goal in October
x Platte River adopted a 100%
non-carbon by 2030
resource diversification
policy in December
x Platte River signed a Power
Puchase Agreement for an
additional 20MW of solar at
the Rawhide Energy Station.
Commercial Operation
anticipated in 2020
x Staff determining next steps
on Green Energy program
options based on planned
changes to Platte River
wholesale rate structure in
2020
x Platte River is in progress on
development of the
Roundhouse wind project
(165 megawatts) and a new
20 megawatt solar facility.
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Attachment: Previous Council Priorities Dashboard, March 2019 (8030 : Council Priorities)
Reduction in energy use at the Drake
Water Reclamation Facility measured in %
change in kWh
Utilities
Next Council Action:
No regular meetings or work
sessions scheduled at this time.
Other Info:
x Procurement of gas
conditioning unit has been
executed.
x Project design is
substantially complete.
Project construction will
begin in June 2019 and
expected to be complete by
end of 2020.
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Attachment: Previous Council Priorities Dashboard, March 2019 (8030 : Council Priorities)
Utilities/
Sustainability
Services /
Planning,
Development,
and
Transportation
Next Council Action:
No regular meetings or work
sessions scheduled at this time
Other Info:
x Core staff team is
developing strategy for
identifying priorities within
this space and to prepare
for Smart Cities Readiness
Grant Application in Winter,
2019.
x Open Data efforts continue
to focus on publishing
frequently requested data,
expanding the inventory of
City-owned data, and
creating new ways for the
public to interact with City
data
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Attachment: Previous Council Priorities Dashboard, March 2019 (8030 : Council Priorities)
potential reset of Industry
Cluster grant funding
anticipated Q1, 2019
x ELT Committee formed to
prioritize implementation
actions
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Attachment: Previous Council Priorities Dashboard, March 2019 (8030 : Council Priorities)
x Developing individual
Council Business Visit
Strategies - Target
Completion end of March
x Sharing the results of the
National Business Survey
internall and externally
ECONOMIC HEALTH
FOCUS - Continue
focus on I-25 buildout
Purpose: Work with CDOT and regional
partners to fund I-25 lane expansion from
Fort Collins to Denver
Outcomes:
x Establish a funding source and
timeframe for completion
Planning,
Development,
and
Transportation
Next Council Action:
No regular meetings or work
sessions scheduled at this time
Other Info:
x A letter of support for the
CDOT INFRA Grant was
prepared and sent to the
U.S. Department of
Transportation encouraging
funding for the I-25
Segments 7 and 8 project.
ATTACHMENT 2 1.2
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Attachment: Previous Council Priorities Dashboard, March 2019 (8030 : Council Priorities)
Financial Sustainability.
x Study sales tax leakage
x Revenue trend identification
and community awareness
x Revenue diversification
x Review City Fees
x Shop Fort Collins
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Attachment: Julia Novak Summary of Council Retreat (8030 : Council Priorities)
improved resilience of the
Poudre River and streams
High Priority EH-3: Air Quality – Local, state,
and federal advocacy. Evaluate
radon working group
recommendations. Pursue
further reductions of City ozone
precursors. Expand community
programs for ozone. Conduct
assessment of the
microparticulate impact on
disparate groups.
x Impact mitigation of high
radon levels
x Reduce ozone precursors
x Understand the prevalence
of microparticulate pollution
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Attachment: Julia Novak Summary of Council Retreat (8030 : Council Priorities)
coordinate with other
organizations.
x Understanding from Council
on the status of efforts
High Priority HC-5: Adopt an equity lens tool
for past and future decision-
making including hiring, boards
and commissions, community
engagement, budgeting, etc. and
consider the CEDAW Resolution
as part of the Equity Lens.
x Understanding disparities in
the community and make
progress to reduce them
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Attachment: Julia Novak Summary of Council Retreat (8030 : Council Priorities)
Packet Pg. 17
Attachment: Julia Novak Summary of Council Retreat (8030 : Council Priorities)
x Grateful
x Trust
x Thoughtful
x Can do attitude
x Authentic
x Polite
x Diligent
x Leader
x Systems thinking
x Clarity and Direction
x Agreeable
x Prepared (x3)
x Accountable
x Flexible
x Open
x Open minded
x Consensus building (x2)
x Grateful
x Support
x Engaged
x Willing to engage
x Collegial
x Friendly and upfront
x Act as a body
x Respect different priorities
x Community-for-all
perspective
x Acknowledges differences
x Articulate
x For the right reasons
x Transparent
x Fair
x Disagree respectfully
x Speak respectfully
x Respectful (x4)
x Honest
x Curiosity
x Trust
x Community listening
x Active listening
x Listens
x Future focus
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Attachment: Julia Novak Summary of Council Retreat (8030 : Council Priorities)
to learning –
engaged with CML
and NLC
x High functioning is
a prerequisite to
high performance
x Focused on local
policy and relevant
action
x Engaged and
collaborative –
externally,
regionally,
nationally
x Trustworthy,
stable, and willing
to change when
appropriate to do
so
x Inclusive
x Active
x Environmental
commitment
x This can be a
question that
drives our
decisions: Will this
decision move us
toward being a
high performing
community FOR
ALL?
x Meet our
community where
THEY are
x Let everyone
THRIVE
x “If it is not for all, it
is not for us.”
x Equitable
x Engages – two-way
– well!
x Engaged, durable
partners who co-
create a high
performing
community
x Effective boards
are intentional
x Each person
achieves
something greater
personally by being
part of this
x Understand how
each person
contributes to the
body
x Identify shared
learning
opportunities
x Be curious – “tell
me more”
x Tapping into the
knowledge of key
stakeholders who
can contribute
expertise
x Build a base level
of knowledge
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Attachment: Julia Novak Summary of Council Retreat (8030 : Council Priorities)