HomeMy WebLinkAbout1999.09.00 - Hendricks and 30th Retention Basin Wetland Revegetation Monitoring Year 2I
I
I
1
I
I
I
I
I
-l
l
J
J
J
J
J
J
J
HenAricts and 30th Street
Retention Basin
\iletland Revegetation Monitoring
Report Year 2
1999
Prepared for
City of Port Townsend
181 Quincy Street
Port Townsend, Washington 98368
Prepared by
Dixie Llewellin
Olympic Wetland Resources, Inc.
856 50th Street
Port Townsend, Washington 98368
?r \s$
\ss
I
I
I
-t
.t
I
Hendricks and 30th Street
Retention Basin
Wetland Revegetation Monitoring
September 1999
Year 2
Contents
1.0 Introduction
1.1 Project History
2.0 Methodology
2.1 Project Goals and Objectives
2.2 MonitoringMethods
2.2.I Determining Survival Rates of Trees, Shrubs, and Emergents
2.2.2 Documenting Wetland Changes With Photographs
2.3 Monitoring Schedule
Table 1. Monitoring Schedule
3.0 Results and Discussion
3.1 Forested Survival
3.2 Scrub/Shrub Survival
3.3 Emergent/ Herbaceous Strvival
3.4 Salvage Effort
3.5 Species To Be Replaced
Table 2. Species To Be Replaced
3.6 Weedy Species
3.7 Action Items
4.0 Summary
Appendix
FiguresI. Monitoring Area and Photopointsil. Tree and Herb Monitoring Form
m. Shrub Monitoring Form
ry Salvaged Plants Monitoring Form
Photopoints
V Photopoints I and 2VI Photopoints 3 and 4
Vtr Photopoints 5, 6a, 6b, and 6c
VItr Hendricks Street Chronology
-l
J
I
!
.-t
!J
!
IJ
J
Hendricks and 30th Street
Retention Basin
Wetland Revegetation Monitoring
Report Year 2
1999
1.0 Introduction
This report summarizes findings from the 1999 Hendricks and 30ft Street Wetland Revesetation
Monitoring project. The purpose of this report is to document the compliance to performance
standards established by the City of Port Townsend for revegetation projects. All species from
the original planting plan are installed on site.
1.1 Project History
The City of Port Townsend constructed a stormwater retention pond in 1997 :r:'the vicinity of a
small depression wetland between 29th and3Oft Street on Hendricks Street. A wetland
delineation (May 1997) documented a 1,300 square foot Category Itr wetland which received
stormwater from up-gradient neighborhood areas. St. Herman's of Alaska Eastem Orthodox
Church was built adjacent to this wetland and has collaborated with this revegetation project.
Native wetland and upland plants were salvaged from the site prior to the construction and
replanted afterwards. Additional native plants which were grown in a nursery were also planted
fuom 1997 to 1999. Through volunteer efforts, 64 trees, 250 shrubs, and over 170 herbaceous
plants have been planted in and around this retention basin.
2.0 Methodology
2.1 Project Goals and Objectives
The goals of the Hendricks and 30ft Street Revegetation Project are to use native plantings to
restore the firnctions and values of the wetland/retention pond buffers, and to restore the habitat
value of the site by planting diverse vegetation in the tree, shrub and herbaceous layers. Native
vegetation, which is tolerant of our local climatic variations was selected for re-vegetating the
site. Priority was given to species already present on the site, thus creating a continuity with the
surrounding plant communities. Vegetation that was previously growing on, and adapted to the
site (hawthoms, willows, sedges and roses) has been reintegrated through major salvage efforts.
2.2 Monitoring Methods
The site is small enough that each individual plant can be counted. Individuals are categorized as
tree, shrub, or emergent/herbaceous. Monitoring forms have been developed to record planting
date, plant survivorship and condition of planted trees, shrubs, and emergents, for plants
purchased at local nurseries and salvaged plants.
1
Olympic Wetland Resources, Inc.
Hendricks and 30th Street Revegetation Monitoring Report
Year 2
September 1999
x
I,i
2.2.1 Determining Survival Rates of Trees, Shrubs, and Emergents
Actual survival percentages were calculated using two methods. The first method compared
numbers of plants observed against total numbers planted. The second method compared the
numbers of plants observed that were alive and healthy to the total numbers observed (dead or
alive). These survival rates are listed on the monitoring forms under totals. Monitoring forms
for each of the plant communities are included in the Appendix (Figure [, il, and tV).
2,2.2 Documenting Wetland Changes With Photographs
Six permanent photopoints were established on site to document the changes of the vegetation
layer over time. A map showing photopoint locations, and the direction photographs were taken,
is included in the Appendix (Figure I). Photopoints #1 through #4 consist of composites of
pictures. Photopoints # 5 and #6a,6b,6c, are of the biofiltration swales and stormwater
overflows. All photographs are included in the Appendix (Figure V, VI, and Vtr).
2.3 Monitoring Schedule
As per City of Port Townsend monitoring requirements, this site will be monitored annually for
three years after final planting is complete. Final planting was completed in 1999. Table 1.
Shows the status of the monitoring schedule:
Table 1. Monito Schedule
3.0 Results and Discussion
The revegetation monitoring goal is to determine whether the performance standards identified
by the City of Port Townsend have been met. Perfonnance standards require that the site is
dominated by a cover of 85% "desirable species" with less thm 15% "weed species" 3 years after
final planting. Survivorship of tree and shrub species is expected to be 80% or greater 5 years
after the final the planting phase. All dead or dying plants should be replaced by the same
species from the original planting plan during the appropriate season. Also all Scot's broom and
reed canarygrass should be completely eliminated from the site.
Data was collected on August 23, L999 by Dixie Llewelin of Olympic Wetland Resources, Inc
A comprehensive count of all trees, shrubs and emergent vegetation was completed. Species
with zero survival rates were not included in the average. Madrona for example, is an
exceptionally difficult species to transplant and no individuals survived; it was not included in
the total average. Percentage survival rates ofplants observed and survival rates ofplants
planted are discussed in the section following.
Olympic Wetland Resources, lnc.
Hendricks and 30th Street Revegetation Monitoring Report
Year 2
I
J
-,1
2
Spring 1999 Fall 1999 Fall 2000 Fall2001 Fall2002Monitoring schedule Fall 1998
10/98 8t99Vegetation and Habitat
Photopoints 10/98 8/99
t2t98 lt/99Annual Report
September 1999
3.1 Forested Survival
The survival rate of trees observed was very good, at 98oh, with a survival rate of 85% for trees
planted. All of the shore pines planted survived and are healthy. However several aspen were
vandalized and only two of the six trees remain. Twenty serviceberry were planted and thirteen
were found during this monitoring period. Many of these trees were small when planted and the
weeds in many locations at the site completely covered the small plants. Mountain ash and vine
maple, which were planted in April 1999, were stressed due to lack of water. The irrigation
system was not activated until August25,1999.
3.2 Scrub/Shrub Survival
The overall survival rate of scrubs was good 9lYo,with a moderate survival rate when counting
all shrubs planted, 65%. Ingeneral, the twinberry, willow, hardhack, snowberry, and dogwood
are adapting to the site. The Iargehazelnut was stressed due to lack of water and several
ninebark shrubs were completely covered with weeds. In April of 1999 many small salal and
kinnikinnik were introduced to the dry banks. These specimens were quite small and received no
care after planting and therefore had very poor survival rates. Junipers and boxwood (mountain
lover), also extremely drought tolerant species were also introduced with good survival rates.
3.3 Emergent/Herbaceous Survival
Survival rate for most emergent species was excellent,l00Yo. Several planted species such as
slough sedge, soft rush, water parsley, and hardstem bulrush are well established and are
reproducing with signs of vigorous new growth. Species planted in the emergent pond area in
1998 that did not survive include sawbeak sedge and tapered rush. We do not recommend
replacing these species since emergent species that are thriving on site are better adapted to
existing conditions. Sword fem, which was planted in the upland areas, did not survive.
3.4 Salvage Effort
The survival rate for salvaged plants varied according to plant type. Trees transplanted included
Madrona and cherry which did not survive the transplant, however the shrubs had an excellent
survival rate, at 94o/o and the emergent/herbaceous species had a good rate at 66Yo.
3.5 Species to be Replaced
Species to be replaced include trees and shrubs that adapt well to the site. If species from the
original plan were unable to adapt to site conditions they have been eliminated and substitutions
have been made. If the planting situation is inadequate due to environmental conditions such as
lack of water or poor soil, conditions, the plan will be altered accordingly while replacing the
plants, by adding mulch and adjusting the inigation system. Plants that have been grown in the
capillary bed can be used to replace dead or dying plants. Table 2. Shows the list of plants to be
replaced:
3
Olympic Wetland Resources, Inc.
Hendricks and 30th Street Revegetation Monitoring Report
Year 2
September 1999
-l
Table 2. Species to be Replaced
CommonName ScientfficName
Trees
Quantrty Size
Serviceberry Amelanchier alnifulia 3 3-4',
Total # of trees to be replaced 3
Shrubs
Hazelnut Corylus cornuta 3 3',
Indian-plum Oemleria cerasifurmis )#2-5
Wax myrtle Myrica califurnica*3 atJ
Oregon grape Berrberis aquifolium*4 #t
Total # of shrubs to be replaced 12
3.6 Weedy Species
Several species of tall grasses (orchard grass and tall fescue) along with curly dock and thistle
have been identified on the site. Mowing or hand pulling these non -natives plants should be
done regularly to ensure the survival of the planted species. No Scots broom or reed canarygrass
were seen during the 1999 survey.
3.7 Action Items
_Weed site (Fall, Spring)
Mow or weed-eat areas without plants (Annually)
Mulch trees and shrubs (Fall 1999)
L:rigation system
1. Activate irrigation as soon as the dry season begins
2. _Check inigation regularly (at least once per month)
3. Tum off irrigation system in late fall
Replace dead or dying plants
4.0 Summary
The majority of salvaging, planting, and maintenance has been conducted by an all-volunteer
work force. In 1998 the first phase of an inigation system was installed which included main
lines and hose bibs. In 1999 the drip inigation was completed but was not activated until August
25 1999. Many trees and shrubs were stressed due to lack of water and were covered with
4
Olympic Wetland Resources, lnc. September 1999
Hendricks and 30th Street Revegetation Monitoring Report
Year 2
I
-t
IIl
weeds. Weeding and watering are recommended for three years after final planting is complete
(until 2002). The survival rate for planted species is good for tree, shrub, and emergent species
(98yo,9lo/, and 100%) for plants observed on site. Replacement plant recommendation are
indicated in Table 2. in Section 3.6.
Although compliance with performance standards for revegetation projects is determined after
three years, the second year progress report for this project is very good, with very high survival
rates in the tree, shrub, and emergent species. Presently the grotrnd cover in several locations on
site is dominated by greater than 50%o undesirable "weed species". The goal of the performance
standards after 3 years is to have less than 150% "weed species". Recommendations made in the
Action Item list in Section 3.7 will help control weeds.
Olympic Wetland Resources, Inc.
Hendricks and 306 Street Revegetation Monitoring Report
Year 2
I
/
Ii.l
i
,j
I
1)
i-)
5
-,/
u/
September 1999
Figures
Appendix
I. Monitoring Area and Photopoints
II. Tree and Herb Monitoring Form
m. Shrub Monitoring Form
IV Salvaged Plants Monitoring Form
PhotopointsV Photopoints I and2
VI Photopoints 3 and 4
VII Photopoints 5, 6a,6b, and 6c
VIII Hendricks Street Chronology
Figure VIII Hendricks and 31*t Street Re-vegetation Chronology
1997
March I
October 4
October 16
October 22
October 23
October 30
1998
February 2l
May 16
June 16
November 7
1999
May I
June
August 25
Salvage Date--Removed all plants to capillary beds
Volunteers spread gtass seed mixture and peat moss
Planted wildflower seed (pearly everlasting, goldenrod, Douglas aster)
Planted emergent, (Carex obnupta, Carex stipata, water parsley, bulrush,
dogwood, willow)
Added Regreen Sterile grass mix
Planted 3 different species of annual non native wildflowers seeds
Moved all plants from salvage beds back to site (sedges and rushes, one large
hazelnut, several hawthorns, oceanspray, Nutka rose, Scoulers willow, spirea)
Planting at Hendricks Street (vine maple, shore pine, sword fern, blue
elderbenies, red flowering currants, hazelnut)
Irrigation and water tap installed
Planting (40 Slough sedge, 30 sawbeak sedge, 30 tapered rush, 30 water-parsley,
l1 serviceberry, 8 hazelnut, 10 oceanspray,ll Indian plum, 7 aspen, 3 hawthorn,
2vrne maple,3 spirea,2 snowberry)
Planting (5 shore prne,2 sequoia, 3 mountain ash, 10 dogwoods, 8 twinberry,
8 ninebark)l0 rose, 15 salmonberry, 11 vine maple, 20 red currant, 10 elderberry,
6 wax myrtle,20 Oregon gape)
Planting (80 kinnikinnick, 10 shrubby cinquefoil, 10 junipers, 10 boxwood,
I 5 evergreen huckleberry)
Drip inigation system completed
System checked, with additional drippers, and activated
l
I
"J
lWeaoRqlvzan
To:Judy Surber
From:Sam Gibboney
Subject: Hendricks Street("Peeping Frog Pond") Monitoring Report
Date:October 29.1999
D. Llewellin, D. Peterson
1. Please find attached the Wetland Revegetation Monitoring Report for Year 2. This
documents reports on restoration efforts that have taken place since August 1998.
2. Thesurvival rates of the trees and scrub-shrub zones are againvery high. The emergent
zone vegetation is doing well and that we are well on the way to meeting the performance
goal of 85%o coverage by desirable species.
3. Other action items are included in the report. I will be meeting with Dave soon to
discuss my workplan and how to accomplish these recommended items.
5. Please feel free to call should you have any questions. Ext. 1158
(1,
CC
D:\SAMVIENDRIKS\mnIr rpt bcd yr2.wpd
'ft'llendrich ond 30+h StreelPlonting Plon ond Photopointr30lh Straetpoint # 5BIOSWALE5HOR,E PINEsALALRuiHPhotoVINE MAPLEPATH/1(9SPIREASALAL\rHAZELNUT/lHAWTHORNLOVEREXI9TINGDOUGLAS FI?sPhotopoint # 1PARK AENCH WTHHONEYSUCKLE YINESTO CHURCHBIOgWALElrl5EOGE5il*. l/zPhotopoint# 4IHMELNUT{/{BIT1ER CHER,RTELDERFERN/OCEANSPR,AY^r.RED \v'HUCKLEEERY /qEDGE5WAX MYRILENINEBARKSHOREPhotopoint# 2Photopoint #6a,b,cjEMERGENC/l\ \rr (\ /1. IUrG\z-WLLOWROSECKINNIKINNIKINDIAN PLUMROSEOR,E@N GRAPETWNAERRTASPENPhtnt#39B-0078lob #:tlienl:-c-w:xr,'.i it$,gL,'i4i'#, . .+,r.rlr",9!ber 1999Fitkelftole:tith:gureI0lympic lllellond Rerourrsr, lnc.llendrickr SlreetRavired Plonting Plon856 50th ltreetPorl lownrend, lllA 98368360 385{432
I
Figure II
Hendricks and 30th Street Vegetation Monitoring Form
Planted
Tree
Common Name Scientific Name
Totals
Totals
* New species added to original planting plan.
** Total plant count includes both salvaged and nursery plants.
(1)
ct
A
RI
e
as
coo)a
cl
.E
a
\oo\
)= t, (J\llO\6iJ o\ o\G,ts-o.trtr\' .r .:EE€.!r(l)(D.HLIv(l)c)E_8 3cnooIt tt +t
Ec).tt.1,0)
a
Date: August 23,1999
Observer: D.Llewellin, Olympic Wetland Resources, Inc.
Comments
trees all vandalized soon after
Comments
Figure II
q)EG'(l)A
I
I
I
I.I
98o/o 85o/o
l00o/o 65oh
ll 2 I
l3
0
ll
3 I
0
2
3 3
s/t6/98 Vine maple Acer circinatum
tU7/98 Serviceberry A me I a nc hi e r al nifol i a *
s/t6198 Madrona Arbutus menziesii*
5/16t98 Shore pine Pinus contorta
tU7/98 Quaking aspen Populus tremuloides
tU7/98 Bitter cherry Prunus emarginata*
4ll/99 Sequoia Sequoia sempervirens*
4/t/99 Mountain ash Sorbus scopulina*
t2 4 t2 92%92%Additional larse trees added in 1999. appear healthv
20 l6 l3 t00%65o/o Original plants small and covered with weeds
0 0 0 Transplants did not survive
ll 6 ll r00%t00%All plants healthy
6 6 3 l00o/o s0%
l0 l0 0 Young trees all vandalized the first year
2 N/A 2 100%l00o/o Healthy
3 N/A 3 t00%100%Stressed from lack of water, system online August 25,99
2/2t/98 Slough sedge Carex obnupta
tt/7/98 Sawbeak sedge Carex stipata*
tU7/98 Tapered rush Juncus acuminatus*
2/2t/98 Soft rush funcus elfusus
4tr/99 Orange honeysuckle Lonicera ciliosa*
4/t/99 Hairy honeysuckle Lonicero hispidula*
t0/22t97 Water parsley Oenanthe sarmentoso*
5/r6198 Sword fern Polystichum munitum**
t0/22/97 Hardstem bulrush Scirpus acutus
20
0
0
4
N
N
45
0
40
2A t7 20 l00o/o l00o/o Once established this species will spread rapidlv
30 30 0 0o/o Not present:this year
30 30 0%Not present this year
2 2 4 100%200o/o This species will spread
5 0%Not planted:
5 0o/o Not planted
50 40 45 l00o/o 90%This speoies will spread
l0 3 0 0o/o Did not sulive the transplant, site too dry
20 20 40 rcO%200%Extremely healthy and spreading
I
I/
Monitoring 1999
Figure III
Hendricks and 30th Street Vegetation Monitoring Form
Shrub Common Name Scientific Name
Totals
* New species added to original planting plan.
** Total plant count includes both salvaged and nursery plants.
!(,
ftl
Lo
{fi.,a
(!
P
(t)
00 0\O\ O\60\
Eocnu1c)
+ra
Observer: D.Llewellin, Olympic Wetland Resources, [nc.
Date: August 23,1999
Comments
I
I
1
II gloh 650/0
Figure III
40 N/A 3 67%5o/o Very small plants did not survive, poor soil and no water
20 N/A 65%t6 8t%Good location, needs more care until established
l0 N/A 9 l00o/o 90%Healthy. sisns of deer grazing
9 8 3 67%22%Sufferine from lack of water and weed cover
ll l0 8 l00o/o 73%Healthy. population from original stock spreading
40 N/A 7 29%5%Received no care after planting, hish mortality
t4 t4 t4 93%93%Small plants, mostly healthy
l0 N/A 9 90o/ol00o/o Small plants, mostly healthy
8 N/A 8 t00%l00o/o Good species for this location
6 N/A I 100%r7%Only plant observed was stressed
4 I I 100%25%Poor survival rate due to weeds and lack of water
l0 N/A 9 78%70%Survival good
8 N/A t0 l00o/o t25%Covered with dense weeds
l0 N/A 7 t00%70o/o Healthy, good location
l0 l0 5 t00%5A%Plant that were located were stressed due to lack of water
8 7 8 t00%l00o/o Once established these plants will spread
l5 N/A 0 0o/o 0o/o Did not transplant
3 3 3 t00%100%Well adapted to this site
l0 l0 7 t00%70o/o Located in hieh traffic location
5 5 5 100%t00%Healthy will spread
l00o/o444100%Well adapted to this dry location on site
l5 N/A 2 t00%t3%Small plants did not receive care after transplanting
6^t99 Kinnikinnik A r c t o s t a p hy I os tu a -ur s i *
51v99 Oregon grape Berrberis aquifolium*
51U99 Red-osier dogwood Cornus sericea*
5lt6198 Hazelnut Corylus cornuta**
97198 Douglas' hawthorn Crataequs dousiasii
6^t99 Salal Gaultheria shallon*
97t98 Ocean-spray Holodiscus discolor**
61v99 Juniper Juniperus communis*
5lll99 Black twinbeny Lonicera involucrata+
5lt/99 Wax mWle Myrica californica*
51U99 Indian plum Oe mler ia ceras iformis *
61v99 Mountain lover Paxistima myrsinites*
slU99 Pacific ninebark P hys ocarpus capitatus *
61v99 Shrubby cinquefoil P otent i I la fruit icos a *
5lt6198 Red currant Ribes sanguineunt
212U98 Nootka rose Rosa ntttkana**
slU99 Salmonberry Rubus spectabilis*
5/t6198 Scoulers willow Salix scouleriana
5lt6/98 Blue elderberry Sambttctts cerulea
slt6198 Hardhack (Spirea)Spiraea douglasii
2l2ll98 Snowberry Symphoricarpos albus
6/v99 Evergreen huckleberry Vaccinittm ovctttutt*
,,3
l3 2
9
2 2 I
8
2 5
l3 I
9 I
8
I I
I
7 )
l0 2
7
5
8
0
3
7
5
4
2
Monitoring 1999
Figure IV
Salvaged Plants Returned to Hendricks and 30th Street
Common Name Scientific Name
Totals
Shrub
Totals
Tree
2/2U98 Madrona Arbutus menziesii
2/2U98 Bitter cherry Prunus emarginata
Totals
.c,o
EA
RI
tstt)
\co\
€o
L0)u)
o
6
E5as
o\0\o\
A
rt{)
E()
.r1Eors
€o\o\
trrt!)
Ec,oso+t
€o0l)G'
fila1t
€efr€{#,4
Obsener: D. Llewellin, Olyrnpic Wetland Resourcesr lnc.
@
Comments
660/o 1060/"
94o/o 93o/o
I
I
I
t
!
I
I
IJ
.ii
Figure IV
2l2ll98 Sloueh sedge Carex obnupta
2/2U98 Soft Rush Juncus effusus
212U98 Sword fem Polystichum munitum
20 t7 T7 20 l00o/o l t8%These plants will spread, healthy
4 2 )4 l00o/o 200%Transplants very hoalthy*
0 I 0 0 0%0%Did not suryive
2t2u98 Hazelnut Corylus cornuta
2/2U98 Douglas'hawthom Crataews dougiasii
212u98 Ocean-spray Holodiscus discolor
2l2ll98 Nootka rose Rosa nutlcana
2t2U98 Scouler willow Salix scouleriana
212v98 Hardhack (Spirea)Spiraea dougldsii
212u98 Snowberry SJtmphoricarpos albus
I I I I t00%l00o/o Large clump stressed due to lack of water
8 1l 10 l0 80%73o/o Native population and salvaged plants healthy
4 I 5 I 5 80o/o 80o/o Some additional plants added with last planting 5/99
8 8 8 8 100%t00%Once established will spread
3 3 2 3 l00o/o 100%Healthy, can withstand droucht
5 5 5 5 rcO%100%Plants healthy
4 4 3 4 l00o/o 100%Additional plants included in last plantine 5/99
0 2 0 0 0%0%Does not transplant well
0 3 0 0 0%0%Does not transplant well
rPercentages greater than 100% represent population that are spreading
Oo/o OV"
Monitoring 1999
Hendricks and 30th Street Fhotopoints #t and #2 August tr999
,r,
TlL__-l_..
-i .F
ffi;ffii.,r$'r',''f_! i. 'rl', :1r..
*.sa
a-:llJir:'
lri";:'
Photopoint #1 East View From Church
.#
'9'
:i
at
t
*
*';ft
ar
f a .r I :l ''''
'+.€F.
lrrit
tf'.,,+l
.t
p -..:
Fhotopoint #2 Retention Fond
Olympic Wetland Resowces, Inc.
I
Figure V.
Hendricks and 30th Street Photopoints #3 and*A August 1999
Photopoint #3 North View From Top Of Mound
Olympic Wetland Resources, Inc.
Photopoint #4 West View
Figure VI.
Hendricks and 30th Street Photopoints #5 and #6a,6b, and 6c August 1999
i
.....":!
Photopoint #64
L
')
l
; 't:
"r'' ,'*'
ii
.\
.E t
l;:i
"li-jia
i .1.."t.-i{L,
Photopoint #5 Biofiltration Swale
t; .
Jl.
Olympio Wetland Resources, Inc.Photopoint #6b
Photopoint #6c
Figure VII.