City Council Meeting: May 22, 2008

Agenda Item: 8-C

To:                   Mayor and City Council

From:              Elaine Polachek, Community Maintenance Director

Subject:          Funding Appropriation for Removal and Replacement of Declining Carob Trees

 

 

Recommended Action

Staff recommends that the City Council appropriate of $395,000 for the removal and replacement of approximately 299 declining carob trees and the specialized pruning of an additional 330 carob trees.

 

 

Executive Summary

As part of the FY 07/08 Community Forest Renewal program, staff conducted a study of mature carob trees throughout the City.  The objective was to determine their health, viability and any risk that could be associated with their declining condition.  The study focused on mature and over-mature carob trees that showed signs of decline and/or a risk potential that could present a liability implication for the City.  Study results indicate that out of the 299 trees that require removal, 97 of those trees pose a significant risk of failure.  Several additional trees require removal and specialized pruning in order to eliminate the risk exposure associated with these trees.  An appropriation of $395,000 is needed to remove, prune and replace these carob trees.  A community meeting was held on May 7, 2008 where a panel of urban forestry experts provided additional information on carobs and answered an array of questions from residents.   It was agreed that staff would re-assess the 202 trees identified for removal and determine whether a phased removal plan for these trees was feasible.  Staff will return to Council once the reassessment is completed to report their findings and provide recommendations for a removal plan.  The public outreach and community education component of this project will continue with presentations to community organizations in May and June.  Residents and merchants within a 300 foot radius of the project areas will be notified of public meetings and community members will be invited to help select the species of replacement trees for the affected areas.


Background

The City’s Community Forest consists of over 33,000 trees along its streets and in its parks.  Planted over the course of the City’s history, these trees are an important component of Santa Monica’s infrastructure and like streets, sidewalks and other City infrastructure, they need to be evaluated and renewed on a regular basis.  This is especially true given that Santa Monica’s forest is aging and many trees are reaching the end of their lifespan. 

 

Prudent urban forest management requires an assessment of a species’ health and structural condition.  That analysis began in 2005 with an evaluation of 517 eucalyptus trees.  As a result of that study by an independent consulting arborist, 77 trees were identified as having a risk of failure and requiring immediate removal to prevent future injuries and/or property damage.  In 2007, a study of 300 Canary Island Date Palms in Palisades Park was undertaken with 44 dead and dying palms identified for removal and subsequent replacement. 

 

Given that the City's Community Forest is aging, an on-going annual renewal and replacement program has been established to perpetuate a healthy urban forest.  As part of the FY 07/08 Community Forest Renewal program, staff contracted with HortScience, an independent consulting arborist, to study 630 carob trees throughout the City to determine their health and viability and any risk that could be associated with their condition.  The Carob Assessment Report is Attachment 1.  The impetus for this study came as a result of several carob tree failures over the past five years.  The study focused on mature and over-mature carob trees that showed signs of decline and/or a risk potential that could present a liability implication for the City.  Study results indicated that 300 carob trees present significant risk of failure and require removal and several additional trees require removal and specialized pruning in order to eliminate the risk exposure associated with these trees. 


Discussion

Carob (Ceratonia siliqua) is a common tree found on Santa Monica’s streets and ranks as the 12th most prevalent species in the City’s tree inventory.  They have a moderate growth rate, are drought-resistant and require little irrigation.  When planted in confined grow spaces their large lateral roots usually displace adjacent pavement.  The displacement of pavement by roots and the associated root pruning requirements limits its value as a street tree.  Carobs are generally pest-free but are highly susceptible to decay fungi.  These decay organisms are more likely to be found in trees that have wounds or have been root pruned for hardscape repair.  The problem becomes compounded in trees that are irrigated in the summer.  The life-span of carobs grown in southern California streetscape settings is unknown.  This is because mature trees often fail due to decay at the base of the trunk, poor structure or general decline in condition.  Over 80% of reported failures for carobs involve decay.  The condition and viability of each carob tree was evaluated and details of its growth and structure were noted.  Over 40% (267 trees) of the 630 trees evaluated were determined to be in poor condition with only 15% (94 trees) found to be in good condition.  A tree in poor condition typically shows signs of dieback in the canopy, sparse foliage, excessive sucker growth along the stems or structural defects.  Trees in poor condition are in a spiral of decline and most likely have only a few remaining years of life.

 

Close to 200 of the surveyed trees had fruiting bodies of decay fungi present along the trunk and branches.  An example is shown in the photo at right. 

 

This fungus finds its way into trees through wounds and digests the tree’s internal structure, reducing the strength of the wood and the stability of the tree. The presence of fruiting bodies of the fungus on the exterior of the tree indicates that internal decay is extensive.

 

The potential of each tree to fail was assessed using a standard risk rating system that is commonly used in the arboriculture industry.  Three components were rated on a scale from 1 to 4 with 4 being the highest.  They are: 1) the likelihood that a failure would take place; 2) the size of the part of the tree most likely to fail and 3) the target below the tree.  The three components were added together to form a composite risk rating that ranges from 3 to 12.  Of the 630 trees that were studied, 98 trees had risk ratings of 10 and above (1 tree with a rating of 12 has already been removed).  This is a clear indication that the carob trees have reached the end of their useful life and need to be removed.  The study also indicates that 267 trees have a remaining life span of 5 years while 63% of them (168 trees) have an expected remaining life-span of less than 2 years. 

 

The photo at right shows a weak carob with poor viability and an off-balanced canopy.  The potential risk of its failure will increase as time passes and the trees like the one in the photo continue to decline.

 

Among the surveyed trees, 267 showed defects in structure, poor branch attachments, canopy dieback, old wounds which have developed into cavities and fungal fruiting bodies of decay fungi.  The photo below shows a tree leaning over the sidewalk with a huge wound running along the length of its trunk. 

Another 40% (279 trees) of the surveyed trees were determined to be in fair condition, yet have the same types of defects that were found in the trees in poor condition.  This means that in order to correct that situation these trees will require specific pruning treatments to eliminate the structural defects which in turn eliminates the potential risk associated with those trees.

 

 

 

 

 

 

The photo at below left shows a healthy appearing tree, but the photo on the right reveals that there are old wounds that have developed into decay pockets which have rendered the tree unstable.  This tree has a risk rating of 11.

 

 


The neighborhoods with the largest quantity of removals with the estimated loss of overall canopy coverage are listed as follows:

1.      12th Street between Montana Ave. and San Vicente Blvd.

      49 trees to be removed out of 146 trees for a 34% loss in canopy

 

2.      10th Street between Montana Ave. and San Vicente Blvd.

      48 trees to be removed out of 131 trees for a 37% loss in canopy

 

3.      Hill Street between between11th St. and 21st St.

      36 trees to be removed out of 160 trees for a 23% loss in canopy

 

4.      Ocean Park Blvd. between 11th St and 21st St.                   

      30 trees to be removed out of 142 trees for a 25% loss in canopy.

 

5.      Lincoln Blvd. between Montana Ave. and San Vicente Blvd.

      29 trees to be removed out of 89 trees for a 33% loss in canopy

 

6.      16th Street between Montana Ave. and San Vicente Blvd.

      20 trees to be removed out of 190 trees for an 11% loss in canopy

 

7.      29th Street between Ocean Park Blvd. and Pico Blvd.

      18 trees to be removed out of 79 trees for a 23% loss in canopy

 

8.      17th Street between Ocean Park Blvd. and Pier Ave.

      17 trees to be removed out of 58 trees for a 29% loss in canopy

 

9.      Franklin Street between Nebraska Ave. and Colorado Ave.

      11 trees to be removed out of 67 trees for an 18% loss in canopy

 

These neighborhoods represent a total of 258 trees that need to be removed with the remaining 41 trees identified for removal located in individual sites throughout the City.


All of the trees that are slated for removal will be replaced as part of this project.  Staff has also taken into account an additional 50 trees that will need to be planted in the immediate vicinity of the tree removals that might be already missing.  This is because in some cases trees have already been removed and have yet to be replaced, or in other cases where residents will request a tree to be planted in an existing vacant tree well that is in close proximity.

 

The report also identifies an additional 330 trees that require specific pruning procedures that will eliminate decayed limbs and correct leaning or off-balanced canopies which normally would not be addressed until their next scheduled pruning cycle.  The individual trees have been identified in the consultant’s report and will be pruned ahead of their regular pruning cycle by in-house and contract crews.

 

Summary of Tree Conditions & Risk Ratings

The carob study clearly shows that the conditions of the trees vary from poor to excellent, yet the vast majority of them are in fair to poor condition.  A summary of the condition and viability of the 630 carobs that were studied is as follows:

 

Expected remaining life span

Dead

or no vitality

 

Poor

 

Fair

 

Good

 

Excellent

 

Total

15 yrs

 

0

0

52

14

68

5 – 15 yrs

 

2

152

32

0

186

2 – 5 yrs

 

97

95

0

0

192

Less than

2 yrs

1

168

15

0

0

184

Total

1

267

264

84

14

630

 

All of the trees with risk ratings of 8 and above are recommended for removal, as well as an additional 13 trees that have a risk rating of 7 but are in very poor condition.  A summary of the risk ratings of the 630 carobs that were studied and identified for removal and specialized pruning treatments is as follows:


 

Risk Rating

Total

Comments

12

1

Tree has already been removed.

11

21

All trees with this rating to be removed.

10

76

All trees with this rating to be removed.

9

83

All trees with this rating to be re-assessed for a possible phased removal.

8

106

All trees with this rating to be re-assessed for a possible phased removal.

7

140

13 of these trees are in very poor condition and are slated for removal

6

110

Scheduled for specialty pruning

5 or less

93

Scheduled for specialty pruning

Total

630

 

 

Environmental Analysis

Recently, Council requested that staff provide information on the environmental trade offs when considering tree removals and their replacements.  Staff is in the process of evaluating these costs and benefits.  Specifically in regards to the environmental services that mature trees provide, staff is assessing what will be lost when they are removed, and then how soon, how much, and when those services will be restored.  This environmental analysis is being conducted by utilizing the City’s electronic street tree inventory information and calculating benefits through the use of new technology developed through the U.S. Forest Service’s Community & Urban Forestry Program.  That program is called STRATUM (Street Tree Resource Tool for Urban Forest Managers) and utilizes current tree inventory data to quantify the current dollar value of annual environmental and aesthetic benefits, energy conservation, air quality improvement, CO2 reduction, storm water control, and impacts on property values.  The analysis will then project the environmental benefits of the replacement trees at the time of replacement, 5 years from replacement and 15 years from replacement.  Removal of the carob trees will need to precede this evaluation, however, to address the risk of potential tree failure.


CEQA Compliance

This project is exempt pursuant to CEQA Guidelines, Section 15301.  This Category Class 1 CEQA exemption includes the maintenance or minor alteration of existing public or private structures, facilities, mechanical equipment or topographical features which involves negligible or no expansion of an existing use. 

 

The non-exclusive list of examples of existing uses that fall within this exemption include “the maintenance of existing landscaping.”  This project, involving the removal and replacement of approximately 299 existing carob trees and the specialized pruning of an additional 330 trees, constitutes routine and prudent maintenance of the City’s existing landscape.  The removal and replacement of trees in poor health or subject to tree failure is necessary to protect pedestrians and the public at large. Given the nature of this project, the removal and replacement of existing trees and the pruning of other existing trees, this project involves no expansion in existing use.

 

This project is also exempt pursuant to CEQA Guidelines, Section 15304 since it consists of minor public alteration in the condition of land which does not involve healthy, mature, and scenic trees.   Instead, this project involves the removal and replacement of trees in poor health or subject to tree failure and the pruning of other existing trees.

 

This project is also exempt pursuant to CEQA Guidelines, Section 15061(b)(3) since the removal of trees that are in poor health or subject to tree failure and their replacement with healthy trees has no possibility of a significant effect on the environment.

 

Contractor Selection

In FY 00/01 the City solicited competitive bids for tree care services (bid number 2835) those bids were opened on May 11, 2001.  Subsequently City Council approved the bid award to West Coast Arborists, Inc. (WCA) on July 10, 2001 (Item 1D on the Agenda).  The bid was awarded for a one year period with nine additional one year renewal options. 

The City is currently in the 7th year of the agreement with 3 additional one year renewal options at the same price terms and conditions.  This work will be added to WCA’s work load at the same price terms and conditions as the original bid.

 

Public Outreach

Public outreach is an important component of this project to educate the community on the importance of removing trees that are in a state of decline or pose a high level of risk to the public.  Staff held a community meeting on May 7, 2008 where a panel comprised of urban forestry experts from across the State presented information about carob trees and responded to questions from community members.  Staff will be making presentations to each of the incorporated neighborhood organizations through the months of May and June 2008.  In addition, staff will meet with representatives from various tree advocacy groups and individual residents.  The information presented to the public will include the following key points:

·        Complete description of the City’s forest, including the age of various trees.

 

·        Urban forestry principles and standards that guide the City’s program.

 

·        Need to diversify Santa Monica’s forest.

 

·        Growth habit of the carob.

 

·        Process of decay and its impact on tree stability.

 

·        Risk assessment protocol.

 

·        Rotational management strategy.

 

·        Proposed replacement strategy and the designation of Tree Selection Committees.

 

Additional public outreach strategies include posting the consultant’s report and a fact sheet on this project on the City’s website, and conducting a press conference in the field that will physically identify defects in the trees.


 

Implementation of Removals & Specialty Pruning Treatments

The first phase of the program is to initiate the removal of 97 trees in poorest overall condition and those with risk ratings of 10 and above.  Removals will begin in July immediately following the public outreach process with the posting of the trees for the standard two week public comment.  Trees that are considered to be too high of a risk to wait for the two week comment period will be removed as soon as possible.  These 97 trees are shown in the attached map in red and are at the following locations: 

10th St. = 10 trees

15th St. = 3 trees

Euclid Av. = 2 trees

Lincoln Bl. = 12 trees

11th St.= 1 tree

16th St. = 9 trees

Franklin St. = 5 trees

Palisades Pk. = 1 tree

12th St.= 10 trees

17th St. = 1 tree

Hill St. = 12 trees

Ocean Park Bl. = 15 trees

14th St.= 1 tree

29th St. = 8 trees

Idaho Av. = 3 trees

Pier Av. = 4 trees

 

Staff estimates 20 – 25 working days to complete the removal of these trees.

 

At the May 7th community meeting, staff committed to re-assessing the 202 trees that have risk ratings of 8 and 9 and are identified for removal.  The Community Forester will re-examine these trees and meet with interested residents to determine whether a phased removal over an extended period of time is feasible.  Staff will report back to Council with findings once their reassessment is completed and will provide recommendations for a possible phased removal plan.  However, with the ultimate goal being public safety, phasing the removals of some trees may not be warranted.

 

The specialty pruning work can begin immediately and will be conducted concurrently with the removals by a separate contract crew.  The pruning work will consist of removing decayed limbs, correcting leaning and off-balanced canopies and standard pruning requirements.  This work will be closely monitored by staff and be done in accordance with the recommendations of the carob study.  Staff estimates the work to be completed in approximately 40 – 45 working days.


Selection and Replacement Process for Street Trees

While some streets already have a replacement species designated by the Community Forest Management Plan (CFMP) with an appropriate tree, other streets will need a new replacement species designated.  The conditions that trigger the process for selecting a new tree species are when a replacement species has not yet identified in the CFMP. 

 

Policy 1.4 mandates that City implement a process for community involvement in the decision making process for when designating or selecting a new species of tree for a three block area or more.  Since the community has a significant interest and involvement in the community forest, public input is greatly desired when selecting street trees.  The processes for community involvement will take into account the varying conditions and situations in the individual neighborhoods. 

 

The following seven member committee will make the determination after public input:

·        the Director of Community Maintenance or designee,

 

·        the Community Forester,

 

·        a staff member from the Planning and Community Development Department,

 

·        a staff member from the Environmental and Public Works Management Department,

 

·        a representative from the Recreation and Parks Commission’s Community Forest Sub-Committee,

 

·        a designated member from the public to be named by the Recreation and Parks Commission.

 

·        a local Arborist from the community.

 

Residents and merchants within a 300 foot radius of the project areas will be notified of public meetings to provide input on the recommended tree species and opportunities for public comment on recommended options will occur at those public meetings. 

Notices for the meetings will be published in the local newspaper, sent to property owners, merchants and residents in the project area as well as other interested members of the community.  Staff estimates that the tree selection process will take 2 – 3 months to process and complete and anticipates planting to begin in the fall season.  Once all the species have been designated and the trees have been tagged in the nurseries the planting process should be completed in approximately 30 working days.

 

Alternatives

If Council chooses not to approve this request for funding, the tree removals and specialty pruning work that must occur will be paid for out of the current tree trimming budget.  This will result in a reduction in the number of trees trimmed next year by 40% which translates to 2,200 fewer trees trimmed in FY 08/09.  Given that the trimming program is currently behind in standards by over 6,000 trees the potential risk associated with that deficit increases.  Council may choose to only authorize funding to remove and prune the carob trees and not to replace any tree that were removed. 

 

Without an additional budget appropriation for replacement trees, new trees would not be planted until funding could be identified for replacement trees in the future.  This would result in an increase in tree vacancies and loss of future environmental benefits.

 

Financial Impacts & Budget Actions

An appropriation of $395,000 is required in account 01576.555010 for the following items:

 

Estimated cost for the removals:              $230,000

Estimated cost for specialized pruning:      $50,000

Estimated cost of tree replacements:       $115,000

Total estimated project cost:                      $395,000

 

Staff is requesting the entire appropriation in FY 08/09 as all of the 299 removals will occur within that fiscal year.  Since there will be a minimal net gain in the number of trees there will not be a significant increase in maintenance costs to the City.

 

Attachment 1 – HortScience Carob Tree Assessment and Summary of Qualifications

Attachment 2 – Map of carob tree locations with risk ratings

Attachment 3 – Santa Monica Waste Recovery & Transfer Station Site Map

 

Prepared by:

Walt Warriner; Community Forest & Public Landscape Superintendent

 

Approved:

 

Forwarded to Council:

 

 

 

 

 

Name

Elaine M. Polachek,

Director, Community Maintenance

 

P. Lamont Ewell

City Manager