HomeMy WebLinkAboutLog211
II Rea
2004
Annual Inventory of
Commercial & Recreational
Shellfish Areas
Department of Health PSP Hotline
1-800-562-5632
www.doh.wa.govlehp/sf/blotoxln.htm
Consumers should note:
Paralytk SheIlflsh Polsonl"i. (PSP or -red tide') and Amnesic
Shellfish PoIsoni"i. (domok actd) are naturally occurrlnB marine
biotoxlIU which are not dostroyed by freezt"i or cooklna,
Map ~ by NancyWeost
omce Qf~ HNlthAbesnentl
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Office of Food Safety & Shellfish
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WASHINGTON STATE DEPARTMENT OF HEALTH
OFFICE OF FOOD SAFETY AND SHELLFISH PROGRAMS
ANNUAL GROWING AREA REVIEW
PREPARED BY: Donald Melvin, Environmental Specialist
AREA: Kilisut Harbor
YEAR ENDING: December 31, 2005
CLASSIFICATION: Approved, Prohibited
ACTIVITIES IN THE GROWING AREA IN 2005:
Samples were collected from the growing area 6 times during the year using the systematic random sampling
method. The area was closed due to biotoxin from 9/27/2005 to 12/6/2005.
ANALYTICAL RESULTS OF WATER SAMPLES:
Table # I summarizes the results of all samples collected from the area. This summary shows that all stations in the
area pass the NSSP water quality standard,
CHANGE IN ACTUAL POLLUTION SOURCES THA T IMPACT THE GROWING AREA:
We currently have no information indicating that the area has new sources of pollution,
CLASSIFICATION STATUS:
181 Well within the classification standards
o Meets standards but some concerns
o Meets standards but threatened with a downgrade in classification
o Fails to meet classification standards
REMARKS AND RECOMMENDATIONS:
Table #1 shows that all stations meet the NSSP water quality standards for approved classification and the area is
correctly classified.
RECE IVED
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TABLE 1
SUMMARY OF MARINE WATER DATA (SRS)
Growing Area: KILlSUT HARBOR
Classification: Approved,Prohibited,Unclassified
From 12/05/2000 To 11/22/2005
FECAL COLIFORM ORGANISMS/100 ML
Station Classification Number Range Geometric Est. 90th Meets Std.
Number of Samples Mean Percentile
10 Approved 31 1.7 - 6.8 1.9 3.0 Yes
11 Approved 31 1.7 -13.0 1.8 3.0 Yes
13 Approved 30 1.7 -4.5 1.7 2.0 Yes
14 Approved 31 1.7 - 4.5 1.7 2.0 Yes
16 Approved 31 1.7 - 2.0 1.7 1.0 Yes
18 Approved 31 1.7 -4.5 1.8 2.0 Yes
19 Approved 31 1.7 - 2.0 1.7 1.0 Yes
20 Approved 31 1.7 - 45.0 2.0 4.0 Yes
21 Approved 32 1.7 - 6.1 1.8 2.0 Yes
22 Approved 31 1.7 -7.8 1.8 2.0 Yes
23 Approved 31 1.7 - 6.8 1.9 2.0 Yes
25 Approved 31 1.7 -13.0 2.2 4.0 Yes
24 Prohibited 31 1.7 - 6.8 1.8 2.0 Yes
172 Unclassified 24 1.7 -4.5 1.7 2.0 "N/A
All tides information is presented
The standard for approved shellfish growing waters is fecal coliform geometric mean not
greater than 14 organisms/100 ml and an estimate of the 90th percentile not greater
than 43 organismsl1 00 ml. The above table shows bacteriological results in relation to
program standards,
* N/A - SRS criteria require a minimum of 30 samples from each station, .
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ANNUAL GROWING AREA REVIEW
WASHINGTON STATE DEPARTMENT OF HEALTH
OFFICE OF FOOD SAFETY AND SHELLFISH PROGRAMS
PREPARED BY: Donald Melvin, Environmental Specialist
AREA: Mystery Bay
YEAR ENDING: December 31, 2005
CLASSIFICATION: Approved, Conditionally Approved
ACTIVITIES IN THE GROWING AREA IN 2005:
Samples were collected from the growing area 6 times during the year using the systematic random sampling
method. The "conditionally approved" area was closed from May 1 through September 30 in accordance with the
management plan. The "conditionally approved" area was sampled 3 times when it was in open status. Elevated
biotoxin levels resulted in a closure from 9/23/05 to 12/6/05.
ANALYTICAL RESULTS OF WATER SAMPLES:
Table #1 summarizes the results of all samples collected from the area. This summary shows that all stations in the
area pass the NSSP water quality standard,
CHANGE IN ACTUAL POLLUTION SOURCES THAT IMP ACT THE GROWING AREA:
We currently have no information indicating that the area has new sources of pollution,
CLASSIFICATION STATUS:
o Well within the classification standards
f8I Meets standards but some concerns
o Meets standards but threatened with a downgrade in classification
o Fails to meet classification standards
REMARKS AND RECOMMENDATIONS:
Table #1 shows that all stations meet the NSSP water quality standards for approved and conditionally approved
classification and the area is correctly classified, The area is listed as "of concern" due to the potential for pollution
from large numbers of boats that moor in Mystery Bay,
RECEIVED
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LOG ITEI\;;
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ANNUAL GROWING AREA REVIEW
WASHINGTON STATE DEPARTMENT OF HEALTH
OFFICE OF FOOD SAFETY AND SHELLFISH PROGRAMS
MANAGEMENT PLAN EVALUATION - BRIEFLY DESCRIBE THE FOLLOWING COMPONENTS:
1. Have all parties involved complied with the conditions in the management plan ............,.,....,..,yes
2, Has reporting been adequate to manage the conditional area ............,.,.......,......,........................Yes
3. Does the area consistently meet approved area criteria when it is open for harvest ....................Yes
4. Has a field inspection of critical pollution sources been conducted..................................,..........Yes
LOG ITEM
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TABLE 1
SUMMARY OF MARINE WATER DATA (SRS)
Growing Area: MYSTERY BAY
Classification: Approved,Conditionally Approved
From 01/10/2001 To 11/22/2005
FECAL COLIFORM ORGANISMS/100 ML
Station Classification Number Range Geometric Est. 90th Meets Std.
Number of Samples Mean Percentile
27 Approved 30 1.7 - 4.5 1.9 2.0 Yes
28 Approved 30 1.7 -13.0 1.9 3.0 Yes
29 Approved 30 1.7 -7.8 2.0 3.0 Yes
30 Approved 30 1.7 -11.0 1.8 2.0 Yes
31 Conditionally 30 1.7 - 4.5 1.9 2.0 Yes
Approved
All tides information is presented
The standard for approved shellfish growing waters is fecal coliform geometric mean not
greater than 14 organisms/100 mt and an estimate ofthe 90th percentile not greater
than 43 organisms/100 ml. The above table shows bacteriological results in relation to
program standards,
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Publication No. 75-e38
WA-17-0020
KILlSUT HARBOR REPORT
by
Allen W. Hoore
Washington State Department of Ecology
September 25. 1975
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KIL ISUT HAJr80R
History
Ki11sut Harbor is formed by Indian Island on the west and Marrowstone Island
on the east. The mouth of the harbor opens to the northwest into Port Townsend.
The south end has historically been open (as shown on Figure 1) with a small
island formed by two channels which converge into one channel 8S it enters Oak
Bay. On May 7, 1792, Mr. Johnstone of Captain George Vancouver's exploration
party of Puget Sound rowed back and forth through the channel. Be 'found the
channel to be navigable for small boats only from half flood to half ebb and was
dry at low water. ' During the late 1880' s and '90' 8 the father of Ralph .Johnson,
a local native, sailed a 30 foot sloop through the channel. Also, cattle scows
were r"..m through the channel.
In 1908 and 1912, bridges were constructed with one across each channel con-
necting Indian Island to Marrowstone Island. There was enough clearance for
navigatiou by rowboat since one or two of the local residents rowed through
on their way to work at fish canneries or for fishing in Oak. Bay until about
1940. Shortly after 1940 the bridges were taken out and large culverts were
installed, In 1958 the large culverts were taken out an.d the currently
existing smaller culverts, approximately three feet in diameter, were in-
stalled. At the same time the road bed was reinforced with fill and riprap
was installed. The smaller culverts nearly completely restricted any
tidal flows compared to the pre-culvert flows.
-1-
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showed us the area in front of his house where the gray water was again
On September 5, 1974, a letter of complaint was written by John O. Taylor,
M. D. to the Department of Fisheries describing a kill of small Dungeness
crabs, cockles and sand dollars along his shoreline property at the east
beach cf southern Kilisut Harbor. Associated with this marine kill was a
foul odor coming from gray, turbid water extending It to ~ mile north of his
house, halfway across the harbor to the west and an undetermined distance to
the south. Dissolved oxygen concentrations in the turbid water were 3.5 to
5.5 ppm. The foul odor was first noted on August 16 through the end of the
month during days of low tides.
This situation again occurred in late August and early September of 1975 but
to a lesser extent. In August 1975 the problem was brought to the attention
of the Department of Ecology_ On September 3, 1975 my assistant, Danel
Anderson and I drove to Kilisut Harbor and met Dr. Taylor at his house. He
occ~-.:;;g. Dead cockles, crabs and sand dollars were found on the beach.
The eelgrass was also dying in large amounts and decaying along with the
dead invertebrates. Water samples were taken on S locations in the harbor.
Figure 2 shows the sample locations and the table lists the lab data.
Results
The low numbers of total and fecal coliforms indicates little or no in-
fluence from any nonpoint sewage in the area. Nutrients were somewhat
normal with the exception of the ammonia which was quite high probably be-
LOG ITEM
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occurs at extreme high tides and on a very limited scale.
cause of the breakdown of the dead invertebrates and eelgrass. Total
phosphates were high with a highest reading of 0.13 ppm at the south end
of the bay. This value could indicate a buildup of nutrients.
Discussion
Examination of historical data and personal interviews shows that a con-
siderable amount of water flowed back and forth through the channel between
Indian Island and Marrowstone Island during high tides. The duration of
flow plus the speed of the flow provided good flushing action. This flushing
between the south end of Kilisut Harbor and Oak Bay has been virtually elimi-
nated by the 1:nstallation of culverts. Not only was the water flow severely
restricted but visual examination shows a buildup of sediment on both sides
of the culvert. As time goes by, more wind and wave caused buildup will
result with perhaps a complete blockage of water exchange between Oak Jay
and 'lllisut Harbor. Before the culverts were installed wind and wave action
and current action apparently were sufficient to prevent further sediment
buildu;. Presently the only water exchange between Oak Bay and Kilisut Harbor
Kilisut Harbor is now essentially a cul-de-sae with poor flushing. Natural
biological conditions create a nutrient buildup in a poorly flushed area
such as this. This is further compounded by the summer north winds which
hold the water in the harbor, further restricting the flushing action. If
the channel at the south end were still open the water would run out through
the channel on an incoming tide decreasing any chance of nutrient buildup.
-3-
LOG ITEM
#----211-
Pag'3~~ot__
Consultat~ons with biologist Ron Westley of the Washington State Department
As the tide starts to run out. the stream direction would reverse and Oak
Bay water would run into Kil1sut Harbor d~luting nutrient buildups. Starting
at the time of culvert installation, When flows were severely restricted and
continuing to the present. as flows are cut even more due to blockage by
sed~t build ups, conditions have favored a buildup of nutrients. The
results of this nutrient buildup have become apparent during the late summer
months of 1974 and 1975. A combination of high water temperature and nutrient
buildup caused by poor flushing coupled with a high sunlight level result in
heavy phytoplankton blooms (red tides). The phytoplankton then die off and
start cecomposing. The decomposition uses up most or all of the oxygen
available in the water which in turn kills off the invertebrates coming in
contact with the water. The dead and decomposing plankton and invertebrates
cause an obnoxious odor. The murky, gray water is probably n~trogenous
deco:position products coming out of solution in the oxygen deficient water.
of 'f:.sheries, Point ~tney Shellfish Lab, and Dr. Clifford Barnes of the
Depa:!:'C.lent of Oceanography, University of Washington, confirm these conclu-
sions.
Conclusions
Tbe conditions which have been causing the red tides and consequent shell-
fish kills during the late summer of 1974 and 1975 will continue and perhaps
intensify as the sediments build up with decomposed materials. The young
Dungeneas crab mortalities may also deplete the commercial crab fishery at
the north end of Kilisut Harbor. The only logical way to reverse these
conditions would be to restore the channels at the south end of Kilisut
LOG ITENi
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constructed over the channels for transportation to Marrowstone Island.
Harbor to the natural depths and widths indicated on the 1880 Coast and
Geodetic Survey chart shown on Figure 1. Bridges would then have to be
-5-
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References
Books
Meany. ;:Or'mond S't Vancouver's Discovery of PuStet Sound,
Binfords and Mort, Portland. Oregon, 1957, p95.
Personal Interviews
Barnes, Dr. Clifford A., Department of Oceanography.
University of Washington, Seattle, Washington 98195
Johnson, Ralph B., Nordland, Washington 98358
Taylor, Dr. John 0., Box 116, Nord1and, Washington 98358
Westley. Ron. Point 'Whitney Shellfish Lab,
Brinnon, Washington 98320
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1972
Soundings in Fathoms
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LOG ITEM
# 1-((
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KlLISUT HARBOR LAB DATA
September 3. 1975
Station 1 2 3 4 5
Time 1015 1045 1110 1120 1150
Total Coliform (Col/lOO ml) <SO <50 < 10 < 10 < 50
Fecal Coliform (Col/lOO mi) Est.
20 <20 < 20 < 2 < 20
N03o-N (Filtered) 0.04 0.04 0.01 0.01 0.01
N02-N (Filtered) ND ND ND ND Nt>>
NR -N (Unfiltered) 0.22 0.17 0.17 0.15 0.17
3
T. Kjeldahl-N (Unfiltered) 0.52 1.5 0.54 0.40 0.80
O-P04-P (Filtered) 0.02 0.03 0.03 0.03 0.03
Total Phos.-P (Unfiltered) 0.05 0.13 0.06 0.06 0.08
Turbidity 1 2 3 4 5
.9-
2o.-:-THE DAILY NEWS,. ,.
Port Angeles, Wash., Wed~, pec~10~ 1975
-' " :
. . ~ .
':T 0" prevent future:." problem~
R as tore "0'10 <wd fercou.rs e
;', :",,; '{J;~' ,';,,'l:;~<~'f~'~;({q'~~~!~f';(~:'?;~,~:,,; :.,. {:. !,:~.,\. , - " ';.>;:>",.": ,:'\_~;~~:':'
~ ~ ..
. " 'i-
PORT TOWNSEND-Restoration of '
. ~=nll=~:F!;lv~ ..'-' d Peninsula e(i~f:' . <i.
~O~~:=~~1:~' ~cg;;:;;.'. ' ,:~;: ':~ ..' ':. . ':: .': \i-~::.\ ,);' " i:~ih::" . :;" " , ',. >;~0~<,~L~ ,:>:'f':::\-. ;(~' ~\
C{u:ility'Investigations section of the,' ,,' "_', '.';' '" ,_ .::~~' " , ~: ',....;.... ,,'.' :j.;:,', "', ',., '..,'.../,'<..,'J,., ,.,' ' :.<;. o!'J.\
Department of Ecology. . <.:, ( .. 'In. 1~108:~ an 0: 1912'~" bridges : were<,-,,:remoVed and culverts installed. In 19$, ...
A copy cf Allen W. Moore's report to' ': cgnstructed, one across' each channel, ",;:;Jhelarge, culverts were removed and;'
the 'department was sent to the, '.connecting Indian and' Marrowsttme:;:.smaller ,culverts,j;three feet. in'"
Jefferson County Commissioners as ' islands. Rowboats could, pass under ~,idiameter, were installed and the road'
well as other state departments which them. _In:,1940,tMbridges were >~bedreinforced. Moore said thumaller:
h2d shown an interest in complaints ," :,'.\':, ' .) , .,.".,;,<:..'. c~ ".
received by Dr. John Taylor and Ralph
B.Jobnson, both of Nordland. , " ,
The conditions causing the: reQ'tides
and consequent shellfi.9b kills in 1974
and 1975 will intensify as long as
sediment continues to build up with I
decomposed materials in the southern
er..d of 'Kilisut 'Harbor, according to
Moore. He also predicts the depletion of
the commercial crab fishery at the
norUl end of the harbor for t~e same
reason. ' '
The only logical way to reverse the
cond\tions is to rcstcre the ,channels at
the south end of th~ harbor to de-plhs
and widths indicated in 1880 charts and
construct. bridges over the channels for
transporta lion to Marrowstone Island.
An early history of the harbor
indicates the south end of the harbor
was open with two channels m~eling
into one ch~nel as the waters entered
Oak Bay. Re'~'Ords show the chan."\e1s
were used by boats and scows,
according to Moore's report.
LOG ITEIV/
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.:':: ' " '. \, :'.': K _Ie' '~ ; '~:." , of' ,,': '-':~,"', ~t:'-~' " '::;:.l'~;:;:.~' ,~; ,;,':" i': ,- ,.' :t,,;,:.,\-: \~ ',>.. ",~. ",;. ,,"
i;{{?~fl€i'ii~,;"I,;!\~Y(~:~~;l,~.1J ~~'tt~JMr,. . .;~l~ij>;:i~
..: culvertS restricted the' tidal fl~{"> ;ii}f !"~o\\;e'd large .un~~is'~' eelgra~ ;~::;;,:t ~d pre~~t:: a' buridup~'Of\J{ritrient..{ ~'1~<' "
, JohnO.:I'aylor,Marrowstone Island",: alsodying. """"", '"" '-j'-' 'which have caused the red tides and the ,'~, .::
,resident" complained:.-, to the:>..' The natural flushing action of water, ' marine kills. " , ; .'" ..~~., ': ';:.~ ,
Department of Fisheries in September:~' flow' between Oak- Bay and Killsut: , County Engineer Ed Bee-leer ;;said ':'
,)974, saying sniall cra~, cockles and Harbor was eliminated with the, Tuesday the mattcrhas been brought to
',:sand "dDllarsalong his' shoreline installation Df the smaller culverts and:",\ the county's attention several times . " > :,'
,properly.; were dying and'~ foul od?r:'\~MDorespeculates that more sedim~V~','Dver the.pa5tJew:yc~s b11~,n~~gbll3\~::;~~?
'; was commgfrom grayturbl~ ~ater m/,;,buildup o~ both sides ofthe culverts will)been done.,-V<i:;':,::/':-i;~;iit,~~H. "}',::,\;, .",'
, Kllisut Harbor...,,; _ c ,::;i'.',' ',..' : Xc..} completely block the .'water cxcha11ge--',}, He said pressures m the future Will. be, ::, .~\ '
.'- Tbe'situationr~edln 1975 toa" between the two bodies of water. :;'~:";';: great e!}ough that county government <"/i~
lesser extent ~ Taylor notified' the,' ,,' ,Restoration _ of ,the-water channels .:will have to consider, l'estorationof the::;;~'_:
Department:.Pf Ecology. lnvestigation.'i~would return the tidal flushing action,; channe1sand Construction o{,bridges..' L';;'>
:~.~' ,. .~.,.- t :?~'~ .'.~".- '....;. ':.'";_ '. . "'. ."~,:"j... - ,.:"<~~ '-~ .,' ~ . r i;i~)~;"')~f ,- ':'. .~.-'~' ,~:.;->,.<:..'.,':; :;,~'';:'~>~~:,~';l'.;.;~ .'- ~~~<'-r~';, .-::~\~.;.,.:". ...:~,)~' ,"~;: ..:' <.--.';':~. ..')~:?:",:.~~,.~~~~ K)'~~.;:~~ "-~,:..~~:'t~~~~:.
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LOG ITEM
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.' ~RE{=lE, D
.~
SANITARY SURVEY
OF
KILISUT HARBOR
MAY, 2001
WASHINGTON STATE DEPARTMENT OF HEALTH
OFFICE OF SHELLFISH PROGRAMS
JHfmSfi~ LUU~1'l m:n
lOG ITEIVI
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MAY, 2001
"
SANITARY SURVEY
OF
KILISUT HARBOR
WASHINGTON STATE DEPARTMENT OF HEALTH
OFFICE OF FOOD SAFETY AND SHELLFISH PROGRAMS
Prepared by:
Bill Cleland, Public Health Advisor
LOG ITEM
# '2L(
Pag'3 ~ 1.~1-ot_.
TABLE OF CONTENTS
SECTION Page
I. Executive Summary ... ............ .... ...... .............................. .... .......... .......,.. .............. .................1
II. Description of Growing Area ..................................................... ............................................1
III. Pollution Source Survey............................................ ........................................................ 1-3
IV. Hydrographic and Meteorological Characteristics ............................................................3-4
V. Water Quality Studies....................,.......,.................................................,............................. 5
VI. Interpretation of Data...........................................,................................................................. 8
VII, Conclusion and Recommendation..................,...................................,................................. 8
TABLES
1. Marine Water Data: From 2/13/1996 To 12/31/2000..........................................................8
2. Marine Water Data: Sampling Stations...... ... ." ... ... ... ... ... ... ... ......... ... ... ...... ." ... .8-22
MAPS
1. Kilisut Harbor Ambient Monitoring Stations... ". ... ... .., .., ... ... ... ... ... .., ... ... ... ... ... .,. .., ... .24
2. Kilsut Harbor Ambient Monitoring Stations... . .. ... ... . .. .. . .. . ... ... ... .., . .. '" ... .. . ... . .. ." ... ... . .25
3.
APPENDICES
A. 2000 Shoreline Survey of the Kilisut Harbor and Mystery Bay Growing Areas......... ..26-36.
LOG 'TEM
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There has been no previous c1assification(s).
I. Executive Summary
Water quality studies and shoreline pollution assessments indicate that Kilisut Harbor meets
the criteria for classification as an Approved shellfish growing area. The major threat to water
quality appears to be an increase in boating activity and the potential for the improper
disposal of sewage. DOH will track boating activity and may impose harvest area restrictions
as appropriate.
II. Description of Growing Area
A. Location map or chart showing growing area
See Maps 1 and 2
B. Description of area
Kilisut Harbor is a semi-enclosed embayment located on the northeastem Olympic
Peninsula in Jefferson County, Washington. It lies between Indian and Marrowstone
Islands and has a maximum depth of 42 feet at mean lower low water. Its opening to
Port Townsend Bay is restricted by a long sandspit and a shallow sill which limits
water circulation. It is a popular boating destination with two state parks and
numerous recreational opportunities. Primary shellfish production consists of native
and manila littleneck clams and Pacific oysters. Historically, a mechanized clam
fishery occurred here using an east coast style hydraulic escalator dredge. This
fishery was terminated in the mid-eighties due to concerns over adverse impacts to
eelgrass beds. Kilisut Harbor has been a major shellfish production area since
before the turn of the century.
C, History of growing area classification
Kilisut Harbor has always been classified as an Approved shellfish growing area.
1. Date of last survey
The previous Sanitary Survey for Kilisut Harbor was completed in May, 1997.
A shoreline survey was completed in September, 2000.
2. Previous c1assification(s) map(s)
III. Pollution Source Survey
A. Summary of Sources and Location
1. Map or chart showing the location of major sources of actual or potential
pollution LOG \TENl
# 1-<11
Pag'3 ~;f_\J~-
Domestic wastes from the overboard disposal of sewage from boats is
potentially a significant problem. Kilisut Harbor is a popular boating
destination with numerous transient and permanent mooring buoys. This
type of pollution is very difficult to identify with routine water quality monitoring
techniques. This practice has been implicated in a number of well
documented shellfish related disease outbreaks in other states. DOH will
continue to track boating activities and may impose harvest area restrictions
if installation of mooring buoys, marinas, or anchorages increases.
...
See figure page 29 in Appendix 1, "2000 Shoreline Survey of the Kilisut
Harbor and Mystery Bay Shellfish Growing Areas".
2. Table of sources of pollution cross referenced to the map
See page 31.
B. Identification and evaluation of pollution sources
1, Domestic wastes (discussion and maps)
On- site sewage treatment and disposal systems treating domestic wastes
are not a factor influencing water quality in Kilisut Harbor. Numerous suspect
systems were identified, but none had the potential to directly impact Kilisut
Harbor.
2. Stormwater
Numerous stormwater conveyances were identified in the shoreline survey.
These have the potential to rapidly carry potential upland pollution directly to
the Harbor. The shoreline survey recommends further evaluation of these
stormwater conveyances. Based on DOH water quality data summaries for
Kilisut Harbor, which show single digit 90th percentile values and geometric
means of less than 3, stormwater is not a significant pollution source.
3, Agricultural waste (farms, feedlots, & slaughterhouse operations)
Eight animals were identified occupying a pasture with a drainage directly
discharging to the marine waters. Agricultural waste potentially could have
an adverse impact, but is not believed to be significant.
4. Wildlife areas
There are approximately 300 deer resident on Indian Island. Resident and
migratory marine birds frequent the waters of Kilisut Harbor, as do marine
mammals (seals). Wildlife is not a significant factor influencing water quality
in Kilisut Harbor.
5.
Industrial wastes
LOG \TEM
:ag'3_~S. .
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-
Indian Island has long been an industrial area used by the United States
Navy. It has numerous well documented areas contaminated by hazardous
waste. One area with documented shellfish contamination is outside the
boundaries of the Approved shellfish growing area of Kilisut Harbor. There
are no outfall pipes discharging hazardous waste to the Harbor. Industrial
waste is not adversely impacting the Approved shellfish growing waters of
Kilisut Harbor.
IV. Hydrographic and Meteorological Characteristics
A. Tides
1. Type
The marine waters of the Pacific Northwest are subject to mixed semi-diu mal
tides that are characterized by a large inequality in the high water heights,
low water heights, or both. There are usually two highs and two lows each
day, but on occasion, the tidal pattem will result in only one high or one low
tide in a single day.
2. Amplitude
Tidal range in this area is from -3 feet to +9 feet.
B, Rainfall
1. Amount
Rainfall in this area averages around 30 inches a year.
3. When
The following table indicates that November, December, January, February
and March receive the highest rainfall totals of the year.
LOG \TEM
# L.lL
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1
Jan
Mar
Ma!:l Jul Sep Oet Nov
Apr Jun Aug Dee
Day of Year
lI..st.......
R..,io...d
C 1 iPwatc
c.....t.....
CHIMACUM 4 S, WASHINGTON (451414)
Period of Record : 6/ 1/1948 to 7/31/2888
1
,.,
.
C
..-l
....
4
c
o
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~
llS
~
....
Q,.
....
u
G)
'-
A-
3
2
o
Feb
4. Identify frequency of significant rainfalls
The following table indicates that there is a 15 to 20 percent probability of a
0.25 inch rainfall in a 24 hour period from Novemberthrough March.
Precipitation Probability by Quantity
CHIMACUM 4 S, WASHINGTON (451414)
Period : 61 1/1948 to 7/31/2000
Probability of 8.25" precipitation.
100
'il0
so
,., 70
N
.... 100
::7l
~ SO
....
..-4 40
....
.0
J 30
0 20
'-
A-
U
Duration
- 1.."Y
o
Jan 1 Mar 1
Feb 1
Ma!:l 1 Jul 1 Sep 1
Apr 1 Jun 1 Aug 1 Oet 1
Day of Year
P...ob<lbilit", of 0.25" p.....dpit..tio... .."..i..., th.. i.....i<:..t".. p"..io"
st....ti...' 0... th.. plott".. ....t... ~MOoth".. with.. 2'il-<l..", ..."......i...' Me..... filt"...
Nov 1 Dee 31
Dee 1
lI..st.......
R..,ioro..l
Cli....t..
c.....t....
~Back to Probability Graph Options
LOG 'TEM
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N/A
C. Winds - Seasonality and effects on pollution dispersion
The predominant winds are from the southwest with velocities occasionally reaching
up to 60 miles an hour. In winter it is not uncommon to have strong northerly winds,
also sometimes reaching gale force.
D. River discharges
There are no rivers or creeks in the area.
1. Volumes
N/A
2. Seasonal
N/A
E. Summary discussion concerning actual or potential effects of transport on pollution
to the harvest area
Pollution originating in the uplands surrounding the growing area would be rapidly
and indirectly transported to marine waters through the 23 surface water drainage
points identified in the shoreline survey. Pollution related to the overboard discharge
of sewage would directly enter marine waters and adversely impact potential
shellfish harvest sites. The enclosed nature of Kilisut Harbor would tend to trap
pollutants and results in a limited degree of flushing.
V. Water Quality Studies
A. Map of sampling stations
See maps 1 and 2
B. Sampling plan and justification
1. Adverse condition sampling
2. Random sampling
As an Approved growing area, Kilisut Harbor is monitored under the
Systematic Random Sampling methodology. Six samples from each station
are collected on a random basis each year. These samples are collected
under a variety of meteorogical and hydrographic conditions. EM
LOG IT
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"
Kilisut Harbor is correctly classified as Approved.
C. Sample Data Analysis and Presentation - Tables containing the basic NSSP
statistics (number of samples, median or geometric mean, and the respective
variability factors)
1. Station by station array - adverse condition or systematic random sampling
See Table 1
2. Daily sampling results and number of samples collected for survey
See Table 2, pages 7 through 21
3. Overall compliance with NSSP criteria
Table 1 indicates that all stations in the Approved growing area meet the
NSSP criteria.
4. Classification of station
VI. Interpretation of Data in Detennining Area Classification - A discussion of how actual
or potential pollution sources, wind, tide, rainfall, etc. affect or may affect water
quality, that will address the following:
A. Effects of meteorologic and hydrographic conditions on bacterial loading
Meteorologic conditions appear to have little effect on water quality in Kilisut Harbor.
An adverse tidal condition has not been identified
B. Variability in the data and causes
The data for Kilisut Harbor has low variability. Isolated elevated fecal coliform counts
are probably related to periods of heavy precipitation.
VII. Conclusions
A. Map or chart showing classification (closure lines, lines separating various
classifications)
See Maps 1 and 2
B. Legal description
N/A
C.
Management plan (if conditionally approved or conditionally restricted)
LOG \TEM
# iff
Pag'3._ ~ 'u1__
(\
Kilisut Harbor will continue to be monitored under the Systematic Random
Sampling methodology.
N/A
D. Recommendations for sanitary survey improvement
1. Monitoring schedule, stations, etc,
2. Comments
LOG 'TEN\
:ag~.}-ttu! .-
7
-
TABLE 1
SUMMARY OF MARINE WATER DATA (SRS)
Growing Area: KILlSUT HARBOR
Classification: Approved,Prohibited,Unclassified
From 02/13/1996 To 12/31/2000
FECAL COLIFORM ORGANISMS/100 ML
Station Classification Number Range Geometric Est. 90th Meets Std.
Number of Samples Mean Percentile
10 Approved 30 1.7 - 4.5 1.7 2.0 Yes
11 Approved 30 1.7.4.5 1.9 2.0 Yes
12 Approved 30 1.7.4.5 1.7 2.0 Yes
13 Approved 30 1.7 - 4.5 1.9 3.0 Yes
14 Approved 30 1.7.2.0 1.7 1.0 Yes
15 Approved 31 1.7.4.5 1.8 2.0 Yes
16 Approved 30 1.7 -7.8 1.8 2.0 Yes
18 Approved 30 1.7 - 6.8 1.8 2.0 Yes
19 Approved 30 1.7 - 33.0 2.0 4.0 Yes
20 Approved 30 1.7 - 31.0 2.0 4.0 Yes
21 Approved 30 1.7 - 2.0 1.7 1.0 Yes
22 Approved 30 1.7 - 4.5 1.8 2.0 Yes
23 Approved 30 1.7 - 4.5 1.8 2.0 Yes
25 Approved 30 1.7 - 7.8 2.0 3.0 Yes
24 Prohibited 30 1.7 - 350.0 2.2 8.0 Yes
All tides information is presented
The standard for approved shellfish growing waters is fecal coliform geometric mean
not greater than 14 organisms/100 ml and an estimate of the 90th percentile not
greater than 43 organisms/100 ml. The above table shows bacteriological results in
relation to program standards.
t All samples have been verified.
LOG \TEM
# 7 [(
pag'3._$!-ut_.
R
TABLE 2
SUMMARY OF SHEllFISH GROWING AREAS
WATER QUALITY STUDY RESULTS
Growing Area: KllISUT HARBOR
Sampling Station Number: 12
Classification: Approved
Sample Date Sample Time Tide Fcoli/100ml Temperature Salinity
02/13/1996 12:10 Ebb 1.7 8 32
05/01/1996 10:46 Ebb 1.7 12 30
08/06/1996 11:08 Flood 1.7 16 32
09/24/1996 13:21 Flood 1.7 14 32
12/03/1996 12:30 Ebb 2 8 30
12/11/1996 13:07 Flood 1.7 7 30
02/04/1991 12:37 Flood 1.7 6 30
04/01/1997 12:04 Ebb 1.7 10 30
OS/21/1997 11:38 Ebb 1.7 15 32
08/26/1997 12:15 Flood 1.7 15 32
09/09/1991 12:40 Ebb 1.7 16 32
11/04/1997 11:42 Ebb 1.7 11 30
01/06/1998 12:16 Ebb 1.1 8 28
03/03/1998 12:17 Ebb 1.8 10 30
06/02/1998 12:30 Ebb 1.7 15 30
08/25/1998 13:12 Ebb 1.1 18 30
09/15/1998 11:50 Flood 1.7 15 32
12/16/1998 13:31 Flood 4.5 9 30
01/26/1999 12:30 Ebb 1.7 7 32
03/24/1999 12:28 Ebb 1.7 10 32
OS/25/1999 11:51 Flood 1.7 13 32
08/03/1999 12:08 Ebb 1.7 16 30
09/08/1999 13:33 Flood 1.7 15 30
12/21/1999 12:32 Flood 2 8 30
02/02/2000 12:57 Flood 1.7 7 30
04/26/2000 12:56 Ebb 1.7 12 30
06/13/2000 13:02 Flood 1.1 12 32
07/20/2000 08:28 Ebb 1.7 15 30
09/06/2000 13:46 Flood 1.7 15 30
12/05/2000 12:03 Flood 1.1 9 30
LOG ITEM
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Pag'3._ Lof.
Q
Growing Area: KILlSUT HARBOR
Sampling Station Number: 14
Classification: Approved
SUMMARY OF SHELLFISH GROWING AREAS
WATER QUALITY STUDY RESULTS
Sample Date Sample Time Tide Fcoli/100ml Temperature Salinity
02/13/1996 12:23 Ebb 1.7 8 32
05/07/1996 11:03 Ebb 1.7 12 30
08/06/1996 11:24 Flood 2 16 32
09/24/1996 13:31 Flood 1.7 14 32
12/03/1996 12:48 Ebb 1.7 7 30
12/11/1996 13:20 Flood 1.8 7 30
02/04/1997 12:54 Ebb 1.7 6 30
04/01/1997 12:20 Ebb 1.7 10 30
OS/27/1997 11:51 Ebb 1.7 15 30
08126/1997 12:26 Flood 1.8 15 32
09/09/1997 12:54 Ebb 1.7 17 30
11104/1997 11:57 Ebb 1.7 11 30
01/06/1998 12:33 Ebb 2 7 28
03/03/1998 12:35 Ebb 1.7 9 28
06/02/1998 12:45 Ebb 1.7 15 30
08/25/1998 13:18 Ebb 1.7 18 30
09/15/1998 12:04 Flood 1.7 16 32
12/16/1998 13:40 Flood 1.7 9 32
01/26/1999 12:50 Ebb 1.7 7 30
03/24/1999 12:45 Ebb 1.7 10 30
OS/25/1999 12:06 Flood 1.7 15 32
08103/1999 12:21 Ebb 1.7 17 30
09/08/1999 13:46 Flood 1.7 15 30
12/21/1999 12:51 Flood 2 8 30
02/02/2000 13:14 Flood 1.7 7 30
04/26/2000 13:09 Ebb 1.7 11 30
06/13/2000 13:13 Flood 1.7 13 32
07/20/2000 08:42 Ebb 1.7 16 30
09/06/2000 14:00 Flood 1.7 15 30
12/05/2000 12:18 Flood 1.7 8 30
LOG ITEM
# 7JJ
Pag '3 ~-'3.L uf ~
10
Growing Area: KILlSUT HARBOR
Sampling Station Number: 15
Classification: Approved
SUMMARY OF SHELLFISH GROWING AREAS
WATER QUALITY STUDY RESULTS
Sample Date Sample Time Tide Fcoli/100ml Temperature Salinity
02/13/1996 12:13 Ebb 1.7 8 32
05/07/1996 10:50 Ebb 1.7 12 30
08/06/1996 11:11 Flood 1.7 16 32
09/24/1996 13:23 Flood 1.7 14 32
12/03/1996 12:34 Ebb 1.7 8 32
12/11/1996 13:18 Flood 1.7 7 30
02/04/1997 13:10 Ebb 1.7 6 30
04/01/1997 12:07 Ebb 1.7 10 30
OS/27/1997 11:40 Ebb 1.7 15 32
08/26/1997 12:24 Flood 1.7 15 32
09/09/1997 12:43 Ebb 1.7 16 32
11/04/1997 11:45 Ebb 2 11 30
01/06/1998 12:20 Ebb 1.7 8 28
03/03/1998 12:20 Ebb 1.7 9 30
06/02/1998 12:32 Ebb 1.7 15 30
08/25/1998 13:28 Ebb 1.7 18 30
09/15/1998 11:52 Flood 1.7 15 32
12/16/1998 13:39 Flood 1.7 9 30
01/26/1999 12:34 Ebb 1.7 7 32
03/24/1999 12:31 Ebb 1.7 10 32
OS/25/1999 11:54 Flood 1.7 14 32
08/03/1999 12:11 Ebb 1.7 16 30
09/08/1999 13:36 Flood 1.7 15 30
12/21/1999 12:37 Flood 4.5 8 30
12/21/1999 12:49 Flood 4.5 8 30
02/02/2000 13:00 Flood 1.7 7 30
04/26/2000 12:59 Ebb 1.7 12 30
06/13/2000 13:04 Flood 1.7 12 32
07/20/2000 08:53 Ebb 1.7 16 30
09/06/2000 13:48 Flood 1.7 15 30
12/05/2000 12:07 Flood 1.7 9 30
LOG ITENi
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11
Growing Area: KILlSUT HARBOR
Sampling Station Number: 22
Classification: Approved
SUMMARY OF SHELLFISH GROWING AREAS
WATER QUALITY STUDY RESULTS
Sample Date Sample Time Tide Fcoli/100ml Temperature Salinity
02/1311996 11:56 Ebb 1.7 8 32
05/07/1996 10:31 Ebb 1.7 11 32
08/06/1996 10:50 Flood 2.7 16 30
09/24/1996 13:08 Flood 1.7 13 32
12/03/1996 12:15 Ebb 2 8 32
12/11/1996 12:53 Flood 2 8 30
02/04/1997 12:20 Flood 1.7 6 30
04/01/1997 11:50 Ebb 1.7 10 30
OS/27/1997 12:02 Ebb 1.7 14 32
08/26/1997 12:04 Flood 1.7 15 32
09/09/1997 12:14 Flood 1.7 15 32
11/04/1997 11:29 Ebb 1.7 11 30
01/06/1998 12:01 Ebb 4.5 10 30
03/03/1998 12:03 Ebb 1.7 10 30
06/02/1998 12:18 Ebb 1.7 14 30
08/25/1998 13:44 Ebb 1.7 18 30
09/15/1998 11:37 Flood 1.7 14 32
12/16/1998 13:21 Flood 1.7 9 32
01/26/1999 12:15 Ebb 1.7 8 32
03/24/1999 12:12 Ebb 1.7 10 32
OS/25/1999 11:36 Flood 1.7 12 32
08/03/1999 11:54 Ebb 1.7 15 30
09/08/1999 13:19 Flood 1.7 13 30
12/21/1999 12:17 Flood 2 9 30
02/02/2000 12:41 Flood 1.7 7 30
04/26/2000 12:40 Ebb 1.7 11 30
06/13/2000 12:50 Flood 1.7 12 32
07/20/2000 08:10 Ebb 1.7 15 30
09/06/2000 13:33 Flood 1.7 13 30
12/05/2000 11:50 Flood 1.7 9 32
LOG 'TEM
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SUMMARY OF SHELLFISH GROWING AREAS
WATER QUALITY STUDY RESULTS
Growing Area: KILISUT HARBOR
Sampling Station Number: 23
Classification: Approved
Sample Date Sample Time Tide Fcoli/100ml Temperature Salinity
02/13/1996 11:51 Ebb 1.7 8 32
05/07/1996 10:26 Ebb 1.7 11 32
08/0611996 10:45 Flood 1.7 16 32
09/24/1996 13:03 Flood 1.7 13 32
12/03/1996 12:11 Ebb 1.7 9 30
12/11/1996 12:42 Flood 1.7 8 30
02/04/1997 12:15 Flood 2 7 30
04/01/1997 11:45 Ebb 1.7 10 30
OS/27/1997 12:07 Ebb 1.7 14 32
08/26/1997 12:00 Flood 2 15 32
09/09/1997 12:06 Flood 1.7 14 32
11/04/1997 11:25 Ebb 1.7 11 30
01/06/1998 11:52 Ebb 4.5 10 30
03/0311998 11:59 Ebb 1.7 10 30
06/02/1998 12:14 Ebb 1.7 13 30
08/25/1998 13:47 Ebb 1.7 18 30
09/15/1998 11:34 Flood 1.7 13 30
12/16/1998 13:19 Flood 4.5 9 32
01/26/1999 12:12 Ebb 4 7 32
03/24/1999 12:08 Ebb 1.7 10 32
OS/25/1999 11:33 Flood 1.7 11 32
08/03/1999 11:50 Ebb 1.7 15 32
09/08/1999 13:16 Flood 1.7 12 30
12/21/1999 12:13 Flood 1.7 9 30
02/02/2000 12:38 Flood 1.7 7 30
04/26/2000 12:33 Ebb 1.7 11 32
06/13/2000 12:46 Flood 1.7 11 32
07/20/2000 08:02 Ebb 1.7 13 28
09/06/2000 13:30 Flood 1.7 13 30
12/05/2000 11:46 Flood 1.7 10 30
LOG ITEM
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Sample Date Sample Time Tide Fcoli/100ml Temperature Salinity
02/13/1996 12:30 Ebb 1.7 8 32
05/07/1996 11:13 Ebb 4.5 13 30
08/06/1996 11:30 Flood 1.7 16 32
09/24/1996 13:38 Flood 2 14 32
12/03/1996 12:54 Ebb 2 7 32
12/11/1996 13:27 Flood 2 7 30
02/04/1997 13:03 Ebb 2 6 30
04/01/1997 12:29 Ebb 1.7 10 30
OS/27/1997 11:28 Ebb 7.8 14 30
08/26/1997 12:40 Flood 1.7 16 32
09/09/1997 13:00 Ebb 1.7 17 30
11/04/1997 12:01 Ebb 4.5 11 30
01/06/1998 12:40 Ebb 2 7 30
03103/1998 12:42 Ebb 1.7 10 30
06/02/1998 12:52 Ebb 1.7 15 32
08/25/1998 13:09 Ebb 1.7 18 30
09/15/1998 12:10 Flood 1.7 16 30
12/16/1998 13:44 Flood 1.7 9 32
01/26/1999 12:57 Ebb 2 7 30
03/24/1999 12:52 Ebb 1.7 10 30
OS/25/1999 12:12 Flood 2 15 32
08/03/1999 12:26 Ebb 1.7 17 30
09/08/1999 13:53 Flood 1.7 15 32
12/21/1999 12:56 Flood 2 8 30
02/02/2000 13:20 Flood 1.7 7 28
04/26/2000 13:13 Ebb 1.7 11 30
06/13/2000 13:18 Flood 2 13 32
07/20/2000 08:48 Ebb 2 16 30
09/06/2000 14:06 Flood 1.7 15 30
12/05/2000 12:25 Ebb 4.5 8 30
LOG ITEM
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SUMMARY OF SHELLFISH GROWING AREAS
WATER QUALITY STUDY RESULTS
Growing Area: KILISUT HARBOR
Sampling Station Number: 25
Classification: Approved
-
Growing Area: KILlSUT HARBOR
Sampling Station Number: 10
Classification: Approved
SUMMARY OF SHELLFISH GROWING AREAS
WATER QUALITY STUDY RESULTS
Sample Date Sample Time Tide Fcoli/100ml Temperature Salinity
02/13/1996 12:04 Ebb 1.7 8 32
05/07/1996 10:39 Ebb 1.7 12 30
08/06/1996 11:00 Flood 1.7 16 30
09/24/1996 13:15 Flood 1.7 14 32
12/03/1996 12:22 Ebb 1.7 8 32
12/11/1996 13:00 Flood 2 7 30
02/04/1997 12:28 Flood 1.7 6 30
04/01/1997 11:58 Ebb 1.7 10 30
OS/27/1997 11:31 Ebb 1.7 15 32
08/26/1997 12:05 Flood 1.7 15 32
09/09/1997 12:31 Ebb 1.7 15 32
11/04/1997 11:36 Ebb 2 11 30
01/06/1998 12:09 Ebb 1.8 8 30
03/03/1998 12:10 Ebb 1.7 10 30
06/02/1998 12:24 Ebb 1.7 15 30
08125/1998 13:37 Ebb 1.7 18 30
09/15/1998 11:44 Flood 1.7 15 32
12/16/1998 13:26 Flood 4.5 9 32
01/26/1999 12:23 Ebb 1.7 8 32
03/24/1999 12:20 Ebb 1.7 10 32
OS/25/1999 11:44 Flood 1.7 13 32
08/03/1999 12:02 Ebb 1.7 16 30
09/08/1999 13:26 Flood 1.7 14 30
12/21/1999 12:24 Flood 1.7 9 30
02/02/2000 12:48 Flood 1.7 7 30
04/26/2000 12:49 Ebb 1.7 12 30
06/13/2000 12:56 Flood 1.7 12 32
07/20/2000 08:20 Ebb 1.7 15 30
09/06/2000 13:40 Flood 1.7 15 30
12/0512000 11:57 Flood 1.7 9 30
LOG ITEM
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Growing Area: KILlSUT HARBOR
Sampling Station Number: 11
Classification: Approved
SUMMARY OF SHELLFISH GROWING AREAS
WATER QUALITY STUDY RESULTS
Sample Date Sample Time Tide Fcoli/100ml Temperature Salinity
02/13/1996 12:07 Ebb 1.7 8 32
05/07/1996 10:43 Ebb 1.7 12 30
08/06/1996 11:04 Flood 1.7 16 32
09/24/1996 13:18 Flood 1.7 14 32
12/03/1996 12:27 Ebb 1.7 8 30
12/11/1996 13:04 Flood 2 7 30
02/04/1997 12:32 Flood 1.7 6 30
04/01/1997 12:01 Ebb 1.7 10 30
OS/27/1997 11:34 Ebb 1.7 15 32
08/26/1997 12:12 Flood 1.7 15 32
09/09/1997 12:36 Ebb 1.7 15 32
11/04/1997 11:40 Ebb 1.7 11 30
01/06/1998 12:13 Ebb 4.5 8 30
03/03/1998 12:14 Ebb 1.7 10 30
06/02/1998 12:27 Ebb 1.7 15 30
08125/1998 13:34 Ebb 1.7 18 30
09/15/1998 11:47 Flood 1.7 15 32
12/16/1998 13:29 Flood 4.5 9 32
01/26/1999 12:27 Ebb 4.5 8 32
03/24/1999 12:24 Ebb 1.7 10 30
OS/25/1999 11:48 Flood 1.7 13 32
08/03/1999 12:05 Ebb 1.7 16 30
09/08/1999 13:30 Flood 1.7 15 30
12/21/1999 12:28 Flood 1.8 9 30
02/02/2000 12:53 Flood 4.5 7 20
04/26/2000 12:53 Ebb 1.7 12 30
06113/2000 12:59 Flood 1.7 12 32
07/20/2000 08:24 Ebb 1.8 15 30
09/06/2000 13:43 Flood 1.7 15 30
12/05/2000 12:00 Flood 1.7 9 30
LOG ITEM
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SUMMARY OF SHELLFISH GROWING AREAS
WATER QUALITY STUDY RESULTS
Growing Area: KILlSUT HARBOR
Sampling Station Number: 13
Classification: Approved
Sample Date Sample Time Tide Fcoli/100ml Temperature Salinity
02/13/1996 12:26 Ebb 1.7 8 32
05/07/1996 11:06 Ebb 1.7 13 30
08/06/1996 11:26 Flood 1.7 16 32
09/24/1996 13:34 Flood 1.7 14 32
12/03/1996 12:51 Ebb 2 7 30
12/11/1996 13:23 Flood 2 7 30
02/04/1997 12:58 Ebb 1.7 6 30
04/01/1997 12:23 Ebb 1.7 10 30
OS/27/1997 11:54 Ebb 4.5 15 30
08/26/1997 12:28 Flood 1.7 15 32
09/09/1997 12:56 Ebb 4.5 17 30
11/04/1997 11:59 Ebb 1.7 11 30
01/06/1998 12:36 Ebb 2 7 30
03/03/1998 12:38 Ebb 1.7 9 30
06/02/1998 12:48 Ebb 1.7 15 30
08/25/1998 13:15 Ebb 1.7 18 30
09/15/1998 12:07 Flood 1.7 16 32
12/16/1998 13:41 Flood 1.7 9 32
01/26/1999 12:53 Ebb 1.7 7 30
03/24/1999 12:48 Ebb 1.7 10 30
OS/25/1999 12:08 Flood 1.7 15 32
08/03/1999 12:23 Ebb 2 17 30
09/08/1999 13:50 Flood 1.7 15 30
12/21/1999 12:54 Flood 4.5 8 30
02/02/2000 13:17 Flood 1.7 7 30
04/26/2000 13:11 Ebb 1.7 11 30
06/13/2000 13:16 Flood 1.7 13 32
07/20/2000 08:45 Ebb 4.5 16 30
09/06/2000 14:03 Flood 1.7 15 30
12/05/2000 12:21 Flood 1.7 8 30
17
Sample Date Sample Time Tide Fcoli/100ml Temperature Salinity
02/13/1996 12:20 Ebb 4.5 8 32
05/07/1996 11:00 Ebb 1.7 13 30
08/06/1996 11:19 Flood 1.7 16 32
09/24/1996 13:29 Flood 1.7 14 32
12/03/1996 12:43 Ebb 1.7 8 30
12/11/1996 13:15 Flood 1.7 7 30
02/04/1997 12:51 Ebb 1.7 6 30
04101/1997 12:16 Ebb 1.7 10 30
OS/27/1997 11:48 Ebb 7.8 15 30
08/26/1997 12:22 Flood 1.7 15 32
09/09/1997 12:50 Ebb 2 16 30
11/04/1997 11:53 Ebb 2 11 30
01/06/1998 12:30 Ebb 1.7 8 30
03/03/1998 12:32 Ebb 1.7 9 28
06/02/1998 12:41 Ebb 1.7 15 30
08/25/1998 13:22 Ebb 1.7 18 30
09/15/1998 12:01 Flood 1.7 16 32
12/16/1998 13:37 Flood 1.7 9 32
01/26/1999 12:47 Ebb 1.7 7 32
03/24/1999 12:42 Ebb 1.7 10 30
OS/25/1999 12:03 Flood 1.7 15 32
08/03/1999 12:19 Ebb 1.7 17 30
09/08/1999 13:44 Flood 1.7 15 30
12/21/1999 12:46 Flood 1.7 8 30
02/02/2000 13:10 Flood 2 7 30
04126/2000 13:06 Ebb 1.7 11 30
06/13/2000 13:11 Flood 1.7 13 32
07/20/2000 08:36 Ebb 2 16 30
09/06/2000 13:57 Flood 1.7 15 30
12/05/2000 12:15 Flood 1.7 8 30
LOG 'TEM
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SUMMARY OF SHELLFISH GROWING AREAS
WATER QUALITY STUDY RESULTS
Growing Area: KILlSUT HARBOR
Sampling Station Number: 16
Classification: Approved
-
Sample Date Sample Time Tide Fcoli/100ml Temperature Salinity
02/13/1996 12:18 Ebb 1.7 8 32
05/07/1996 10:57 Ebb 1.7 12 30
08/06/1996 11:15 Flood 6.8 16 32
09/24/1996 13:27 Flood 1.7 14 32
12/03/1996 12:40 Ebb 1.7 8 30
12/11/1996 13:12 Flood 2 7 30
02/04/1997 12:45 Ebb 1.7 6 30
04/01/1997 12:12 Ebb 1.7 10 30
OS/27/1997 11:46 Ebb 2 15 30
08/26/1997 12:19 Flood 1.7 15 32
09/09/1997 12:48 Ebb 1.7 16 30
11/0411997 11:50 Ebb 1.7 11 30
01/06/1998 12:26 Ebb 1.7 8 28
03/03/1998 12:29 Ebb 1.7 10 30
06/02/1998 12:37 Ebb 1.7 15 32
08/25/1998 13:25 Ebb 1.7 18 30
09/15/1998 11:58 Flood 1.7 16 32
12/16/1998 13:35 Flood 1.7 9 32
01/26/1999 12:43 Ebb 1.7 7 32
03/24/1999 12:38 Ebb 1.7 10 30
OS/25/1999 12:00 Flood 1.7 15 32
08/03/1999 12:16 Ebb 1.7 17 32
09/08/1999 13:42 Flood 1.7 15 30
12/21/1999 12:43 Flood 2 8 30
02/02/2000 13:07 Flood 1.7 7 25
04/26/2000 13:04 Ebb 1.7 11 30
06/13/2000 13:08 Flood 1.7 12 32
07/20/2000 08:33 Ebb 1.7 15 30
09/06/2000 13:54 Flood 1.7 15 30
12/05/2000 12:13 Flood 1.7 8 30
SUMMARY OF SHELLFISH GROWING AREAS
WATER QUALITY STUDY RESULTS
Growing Area: KILlSUT HARBOR
Sampling Station Number: 18
Classification: Approved
1<)
-
Growing Area: KILlSUT HARBOR
Sampling Station Number: 19
Classification: Approved
SUMMARY OF SHELLFISH GROWING AREAS
WATER QUALITY STUDY RESULTS
Sample Date Sample Time Tide Fcoli/100ml Temperature Salinity
02113/1996 12:15 Ebb 1.7 8 32
05/07/1996 10:53 Ebb 1.7 12 30
08/06/1996 11:13 Flood 2 16 32
09/2411996 13:25 Flood 1.7 14 32
12103/1996 12:37 Ebb 2 8 32
12111/1996 13:10 Flood 1.7 7 30
0210411997 12:41 Ebb 1.7 6 30
04101/1997 12:10 Ebb 1.7 10 30
OS/27/1997 11:43 Ebb 1.7 15 32
08/26/1997 12:17 Flood 1.7 15 32
09/09/1997 12:45 Ebb 1.7 16 30
11/0411997 11:47 Ebb 2 11 30
01/06/1998 12:23 Ebb 1.7 8 28
03/03/1998 12:24 Ebb 1.7 9 30
06/0211998 12:34 Ebb 1.7 15 30
08/25/1998 13:31 Ebb 2 18 30
09/15/1998 11:55 Flood 2 15 32
12116/1998 13:33 Flood 1.7 9 32
01/26/1999 12:38 Ebb 1.7 7 32
03/24/1999 12:35 Ebb 1.7 10 30
OS/25/1999 11:58 Flood 1.7 15 32
08/03/1999 12:14 Ebb 1.7 16 30
09/08/1999 13:37 Flood 33 15 30
12121/1999 12:40 Flood 1.7 8 30
02102/2000 13:03 Flood 1.7 7 12
04126/2000 13:02 Ebb 1.7 11 30
06/13/2000 13:06 Flood 1.7 12 32
07/20/2000 08:31 Ebb 1.7 15 30
09/06/2000 13:51 Flood 6.8 15 30
12/05/2000 12:10 Flood 1.7 9 30
70
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Growing Area: KILlSUT HARBOR
Sampling Station Number: 20
Classification: Approved
SUMMARY OF SHELLFISH GROWING AREAS
WATER QUALITY STUDY RESULTS
Sample Date Sample Time Tide Fcoli/100ml Temperature Salinity
02/13/1996 12:33 Ebb 1.7 8 30
05/07/1996 11:18 Ebb 1.7 12 28
08/0611996 11:33 Flood 1.7 17 32
0912411996 13:42 Flood 1.7 14 32
12/0311996 12:58 Ebb 7.8 7 32
12/1111996 12:48 Flood 2 8 30
02/0411997 13:15 Ebb 1.7 6 30
0410111997 12:35 Ebb 1.7 10 30
0512711997 11:24 Ebb 1.7 14 32
0812611997 12:43 Flood 4.5 16 32
0910911997 13:06 Ebb 1.7 16 30
1110411997 12:05 Ebb 1.7 11 30
0110611998 12:44 Ebb 31 7 30
0310311998 12:46 Ebb 1.7 10 30
06102/1998 12:55 Ebb 1.7 15 30
0812511998 13:05 Ebb 1.7 18 30
0911511998 12:14 Flood 1.7 16 30
12/1611998 13:47 Flood 2 9 32
0112611999 13:01 Ebb 1.7 7 30
0312411999 12:56 Ebb 1.7 10 30
0512511999 12:15 Flood 1.7 13 32
0810311999 12:30 Ebb 1.7 17 32
09/0811999 13:58 Flood 1.7 15 32
12/2111999 12:59 Flood 1.7 8 30
02/02/2000 13:23 Flood 1.7 7 30
0412612000 13:15 Ebb 2 12 30
0611312000 13:21 Flood 1.7 13 32
0712012000 08:51 Ebb 2 16 30
0910612000 14:09 Flood 1.7 15 30
12/0512000 12:28 Ebb 2 8 30
LOG ITEM
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11
Growing Area: KILlSUT HARBOR
Sampling Station Number: 21
Classification: Approved
SUMMARY OF SHELLFISH GROWING AREAS
WATER QUALITY STUDY RESULTS
Sample Date Sample Time Tide Fcoli/100ml Temperature Salinity
0211311996 12:00 Ebb 1.7 8 32
05/07/1996 10:35 Ebb 1.7 11 32
08/06/1996 10:56 Flood 1.7 16 32
0912411996 13:11 Flood 1.7 13 32
12103/1996 12:19 Ebb 1.7 8 32
12111/1996 12:58 Flood 1.7 8 30
0210411997 12:24 Flood 1.7 6 30
04101/1997 11:54 Ebb 1.7 10 30
05/27/1997 11:58 Ebb 1.7 14 30
08/26/1997 12:06 Flood 1.7 15 32
09/09/1997 12:22 Flood 1.7 15 32
11/0411997 11:32 Ebb 1.7 11 30
01/06/1998 12:05 Ebb 1.7 9 30
03/03/1998 12:07 Ebb 1.7 10 30
06/0211998 12:21 Ebb 2 15 30
08/25/1998 13:40 Ebb 1.7 18 30
09/15/1998 11:40 Flood 1.7 15 32
1211611998 13:23 Flood 1.7 9 32
01/26/1999 12:20 Ebb 1.7 8 32
03/2411999 12:16 Ebb 1.7 10 30
05/25/1999 11:40 Flood 1.7 12 32
08/0311999 11:58 Ebb 1.7 16 30
09/08/1999 13:23 Flood 1.7 14 32
1212111999 12:21 Flood 1.7 9 30
0210212000 12:45 Flood 1.7 7 30
04126/2000 12:45 Ebb 1.7 11 30
06/13/2000 12:53 Flood 1.7 12 32
07/20/2000 08:15 Ebb 1.7 15 30
09/06/2000 13:36 Flood 2 13 30
1210512000 11:54 Flood 2 9 30
n
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SUMMARY OF SHELLFISH GROWING AREAS
WATER QUALITY STUDY RESULTS
Growing Area: KILlSUT HARBOR
Sampling Station Number: 24
Classification: Prohibited
Sample Date Sample Time Tide Fcoli/100ml Temperature Salinity
02/13/1996 11:45 Ebb 1.7 8 30
05/07/1996 10:22 Ebb 1.7 10 32
08/06/1996 10:40 Flood 1.7 14 32
09/2411996 13:00 Flood 1.7 13 32
12/03/1996 12:07 Ebb 1.7 9 32
12/11/1996 12:33 Flood 1.7 8 30
02/0411997 12:10 Flood 7.8 7 30
04101/1997 11:41 Ebb 1.7 10 30
05/27/1997 12:10 Ebb 1.7 14 32
08/26/1997 11:57 Flood 1.7 15 32
09/09/1997 12:01 Flood 1.7 14 32
11/0411997 11:21 Ebb 1.7 11 30
01/06/1998 11:49 Ebb 7.8 10 30
03/03/1998 11:56 Ebb 2 10 30
06/02/1998 12:11 Ebb 1.7 13 32
08/25/1998 13:50 Ebb 1.7 17 30
09/15/1998 11:31 Flood 1.7 13 30
12/1611998 13:15 Flood 350 9 32
01/26/1999 12:08 Ebb 1.7 7 32
03/2411999 12:04 Ebb 1.7 10 30
05/25/1999 11:30 Flood 1.7 11 32
08/03/1999 11:46 Ebb 1.7 15 32
09/08/1999 13:13 Flood 1.7 12 32
12/2111999 12:09 Flood 1.7 9 30
02/02/2000 12:35 Flood 1.8 7 30
04126/2000 12:26 Ebb 1.7 11 30
06/13/2000 12:43 Flood 1.7 11 32
07/20/2000 07:58 Ebb 1.7 13 28
09/06/2000 13:27 Flood 1.7 13 30
12/0512000 11:43 Flood 1.7 10 32
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C KIUSUT HARBOR (N)
AMBIENT
MONITORING
STATIONS
7/28/2000
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KILI5UT HARBOR
AMBIENT
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-September 2000-
APPENDIX A
2000 SHORELINE SURVEY
OF THE
KILISUT HARBOR & MYSTERY BAY
SHELLFISH GROWING AREAS
Prepared by:
Scott Berbells
Public Health Advisor
Summary
One-hundred-twenty-nine structures, 23 surface water drainage points, 6 small
agricultural practices, 1 state park and 4 military waste generation/disposal sites were
evaluated during a routine shoreline survey of the Kilisut Harbor and Mystery Bay
shellfish growing areas. Overall, no direct or indirect discharges of waste from on-site
sewage systems or military waste generation/disposal sites were identified that would
result in a downgrade of the classification of the growing areas.
Ongoing evaluation of the area, by the Washington State Department of Health, is
recommended. The evaluation should specifically be directed at the discharge of runoff
to the Mystery Bay area. Furthermore, the Department should continue the evaluation
of boat mooring activities occurring in Mystery Bay and the waste generation/disposal
site remediation activity occurring on Indian Island.
Introduction
Between August 1999 and September 2000, a routine shoreline survey was performed
around the Kilisut Harbor and Mystery Bay shellfish growing areas. The Kilisut Harbor
growing area is bordered by Indian Island on the west and Marrowstone Island on the
east. The Mystery Bay shellfish growing area is located along the western shore of
Marrowstone Island. Both areas are located within Jefferson County. With the
exception of a small area around the Mystery Bay State Park dock, both areas are
classified as APPROVED. Between May 1 and September 30 of each year, the
tidelands located 285 yards parallel to the shoreline in each direction from the state park
dock, and 105 yards perpendicular to the shoreline as measured from the center of the
moorage area is classified as CONDITIONALLY APPROVED due to the presence of
recreational and live-aboard vessels in the area. This CONDITIONALLY APPROVED
area is open for harvest between October 1 and April 30 of each year.
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Washington State
Department of Health, Office
of Food Safety and Shellfish
Program (the Department)
staff members Tom Gibbs,
Cathy Barker and Scott
Berbells surveyed the 10.03
miles of shoreline comprising
the Kilisut Harbor growing
area and the 3.18 miles of
shoreline comprising the
Mystery Bay shellfish
growing area. The location
of the growing areas and the
shoreline survey area are
shown in Figure 1. The
areas were surveyed as part
of the routine, 12-year
growing area evaluation to
assess the actual and
potential pollution sources
that may affect the growing
areas. The survey team evaluated the drainageways, on-site sewage systems,
agricultural practices and other activities that could potentially have an adverse effect on
the classification of the area. Each of the potential pollution sources identified were
classified according to the following categories:
Figure 1
Shoreline Survey
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Direct Impact - A IIDirect Impact" is a pollution source that is defined by the
National Shellfish Sanitation Program (NSSP) as any waste discharge that has an
immediate adverse effect on the growing area.
Indirect Impact - An IIlndirect Impact" is a pollution source that is defined by the
NSSP as any waste discharge that reaches the growing area in a roundabout
way.
Potential Source - A "Potential Sourcell is a pollution source that may influence
water quality in the area. Inadequate setbacks, neglect or abuse of sewage
disposal systems, overgrazed pastures and large numbers of wildlife are
examples that could cause a site to be identified as a potential source of
contamination.
No Impact - The potential source is managed via proper on-site sewage practices
or treatment methods so that there is no negative impact on wres&U~M
# 7--0
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4865 Flagler Road THROUG 8865 Flagler Road
H
64 Griffiths Point THROUG 1640 Griffiths Point
Road H Road
61 Heinzinger Road THROUG 85 Heinzinger Road
H
191 Madrona Road THROUG 211 Madrona Road
H
263 Mumbry Road THROUG 269 Mumbry Road
H
140 Smith Road THROUG 344 Smith Road
H
The individual properties evaluated include those on the western shore of Marrowstone
Island, as described below:
At the conclusion of the evaluation of each property, the inspection was classified as
"complete" or "limited". An inspection was considered "complete" when the location of
the on-site sewage system was identified via the property owner, county records or
returned survey forms. An inspection was considered "limited" when staff made visual
observations, however, the property owner was not interviewed and the exact location of
the on-site sewage system could not be verified.
Also included in this shoreline survey is the eastern shoreline of Indian Island. According
to an Agency for Toxic Substances and Disease Registry (ATSDR) report, the United
States Navy purchased Indian Island in 1939 for use as a storage site for explosives,
seaplanes and antisubmarine cable nets. Since that time a variety of hazardous
materials have been handled, stored and disposed of on the island resulting in soil,
groundwater, surface water, sediment and shellfish contamination. Currently the Navy
uses the island to receive, store, segregate, maintain and issue Naval ordnance.
The Soil Survey of Jefferson County Area, Washington published by the United States
Department of Agriculture, Soil Conservation Service describes the soil typical to the
developed shoreline of Marrowstone Island as Cathcart gravelly silt loam, 0 to 15
percent slopes. Characteristics of this soil include moderate permeability, excessive
slopes in areas and bedrock located between 24 and 40 inches of the ground surface.
Typical soils found on the eastern shoreline of Indian Island include Cathcart gravelly silt
loam, 0 to 15 percent slopes, as described above; Whidbey gravelly sandy loam, 0 to 15
percent slopes; and Alderwood gravelly sandy loam, 0 to 15 percent slopes.
Characteristics of the Whidbey and Alderwoods soil types include moderately well
drained soil above a cemented layer located at a depth of 20 to 40 inches.
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Results
Western Shoreline of Marrowstone Island
The systems of drainageways encompassing the western shore of Marrowstone Island
were evaluated during this survey. A system of twenty-three culverts direct runoff under
roads and directly or indirectly into Kilisut Harbor and Mystery Bay. Seven of these
culverts drain directly into Kilisut Harbor or Mystery Bay while eight provide indirect
drainage to the areas. This information is illustrated in Figure 2. A description of the
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location of each culvert and its relationship to the growing area can be found in
Appendix A. Drainage points D7, D10 and D11 provide direct drainage from small
hobby farms in the area. Drainage points D13 and D14 supply runoff to a natural
drainage way that travels though an agricultural pasture containing approximately eight
animals, before discharging below the Smith Road area. Drainageway D21 pro)lid.es Wl-M'
indirect discharge from a small agricultural area. LUG II t:.
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Legend
. Direct Discharge
.. Drainage Direction
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Figure 2
Kilisut Harbor / Mystery Bay Drainage
One-hundred-twenty-nine of the 136 properties located within the survey area, along the
western shoreline of Marrowstone Island, were evaluated during this survey. Seventy-
four of the evaluations were "complete" while fifty-five were "limited". The use of these
properties can be defined as follows:
Table 1
On-Site Sewage System Evaluation Summary
Use
Full-Time Residential
Vacation
Vacant
Commercial
Recreational
TOTAL
Total Evaluated
69
56
2
1
1
129
Percentage
53
43
2
1
1
100
There were no direct or indirect discharges to the growing area from any of the on-site
sewage systems evaluated in this survey area. Eighty-nine of the on-site sewage
systems were classified as "No Impact", fifteen were designated as "Potential Sources",
and twenty-five were not classified because the system was not located and the
questionnaire was not returned. Table 2 details the on-site sewage systems designated
as a "Potential Source". None of these systems are believed to impact the growing area
at this time.
One recreational shellfish harvesting beach, Mystery Bay State Park, is located within
the growing areas. This park consists of 10.09 acres and 685 feet of saltwater shoreline
along Mystery Bay. The park provides 4 picnic sites, a boat dock with overnight
moorage, 7 mooring buoys, a sewage pumpout station for vessels, a boat launch and 2
vault toilets. As described previously, the area in the vicinity of the dock is closed to the
commercial harvesting of shellfish between May 1 and September 30 of every year.
During the shoreline evaluation of Mystery Bay, moorage information was recorded and
is illustrated in Table 3. In June 2000 the Department authored a letter to the Jefferson
County Department of Community Development regarding the impending approval of
additional mooring buoys within Mystery Bay. The Department recommended tha~ E'Io.'
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1. "Evaluation of the existing DNR moorage's in the bay is complete, and
2. The carrying (assimilative) capacity of the bay is evaluated for potential
wastes from moored boats."
following processing of five pending moorage applications, a moratorium be placed on
additional moorage approval in the bay until:
Table 2
On-Site Sewage System Status
Site Address System Comments
# Status
29 7835 Flagler Road Potential Drainfield located in wet area.
Source System is approximately 20 years
old.
16A South of 7663 Flagler Potential Old system serving vacation
Road Source structure located within 50 feet of
the shoreline. Sanican located
behind house.
17 A 6945 Flagler Road Potential Saturated area around drainfield
Source lateral. Grey water disposed in
separate system.
21 A 1511 Flagler Road Potential System located approximately 50
Source feet from the shoreline. Excessive
growth over drainfield laterals.
26A 1405 Griffiths Point Potential Old recreational vehicle on site,
Road Source May use cesspool for sewage
disposal.
39 7015 Flagler Road Potential Drainfield located within 50 feet of
Source the shoreline.
40 7013 Flagler Road Potential Drainfield located within 50 feet of
Source the shoreline.
31A 1223 Flagler Road Potential Old recreational vehicle on-site. No
Source sewage system located. RV cannot
be moved for pumping.
39A 991 Griffiths Point Potential Old recreational vehicle on-site. No
Road Source sewage system located. RV cannot
be moved for pumping.
45 1481 Griffiths Point Potential Drainfield located approximately 50
Road Source feet from the shoreline. Two
residential structures using one on-
site sewage system.
58A 170 Smith Road Potential Older recreational vehicle on-site.
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Table 3
Mystery Bay Vessel Moorage
Date Vessels at dock Moored in bay
(Mystery Bay State
Park)
~31m9 15 17
9/30/99 14 17
10/13/99 17 18
8/9/00 10 21
8/28/00 5 20
917/00 6 16
9/11/00 4 18
Six small agricultural practices were identified during this survey. These hobby farms
consisted of a small number of animals ranging from two horses to twelve cows. No
animals were located on three of the identified agricultural sites during this evaluation.
These small farms utilize the following drainages, as defined above: 06, 010, 011, 021,
and the wetland drainage located below 013 and 014.
Source Test holes dug for new on-site
sewage system.
67A 6033 Flagler Road Potential Excessive vegetative growth over
Source drainfield, Driveway located over
portion of drainfield.
68A 6031 Flagler Road Potential Septic tank located on the shoreline.
Source
71A South of 5945 Flagler Potential Pit privy located within 50 feet of the
Road Source shoreline.
72A South of site # 71 A Potential Pit privy located within 50 feet of the
Source shoreline.
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Eastern Shoreline of Indian Island
Figure 3
Indian Island Waste Disposal
The eastern shoreline of Indian Island is currently undeveloped. All human waste
generated within the structures located on this island are discharged through a small
sewage treatment plant located on the western shore of the island. The island supports
a wildlife population consisting of approximately 300 deer. These animals have access
to the shoreline, however, are primarily found away from the shoreline.
In 1998 the A TSDR published a report that evaluated the public health hazards
associated with numerous waste generation and/or disposal sites on the island. Four of
these sites are in the vicinity of the Kilisut Harbor shellfish growing area and are
discussed below. The locations of these sites are illustrated in Figure 3.
. Site 10 - This site was utilized
by the Navy as a landfill
from 1945 until the mid-
1970s. According to the
A TSDR report, materials
disposed of at this site
include zinc sludges,
waste paints and thinners,
solvents, strippers, waste
petroleum oil and
lubricants, sandblasting
paint residues, waste oil,
batteries, unidentified
liquid waste, bomb
ordnance and incinerator
ash, asbestos, submarine
nets, polyurethane resins
and residential trash. The
report further states that
contaminants from Site 10
have been introduced to
the marine environment via
direct erosion, surface
water runoff and
groundwater discharge. In 1997 the Navy placed a geogrid liner over the top of
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. this landfill to protect against surface/rainwater infiltration. A passive methane
collection and venting system was also installed within the landfill. The landfill
contains no bottom liner or leachate collection system. In 1988 the Navy banned the
harvest of shellfish in the vicinity of Site 10. This site is located outside the
APPROVED Kilisut Harbor shellfish growing area.
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. Site 12 - According to the A TSDR report, Site 12 was used between the 1940s and
1950s for ordnance disposal and in the most recent past as a pistol range. In 1994
and 1995 approximately 1,800 tons of soil, metal slag, ordnance debris and bomblets
were excavated and screened. Approximately 320 tons were properly disposed of
offsite,
. Site 21 - This site was utilized as a disposal location for waste oils, solvents,
electrical equipment and paint. As per the A TSDR report, the Washington State
Department of Ecology, United States Environmental Protection Agency and the
Navy are currently analyzing groundwater monitoring data to determine if future
remediation is necessary.
. Site 34 - The A TSDR reports that this area was used as an ordnance burn/ordnance
detonation area from the late 1970s to approximately 1990. The area was used to
burn and detonate ammunition and explosives in open unlined pits from the 1970s to
1988. Soil evaluation detect the presence of high levels of lead, total petroleum
hydrocarbons and PAHs, however, the contaminants did not impact ground or
surface water. Soil removal activities were completed in 1996. The area continues to
be utilized to burn obsolete and unstable ordnance, however, the practice is
conducted within enclosed containers and the residual material is properly disposed
of.
According to representatives of the Navy, Sites 10 and 34 have ongoing assessment
and/or remediation activities occurring.
Conclusions
Overall, no direct or indirect discharges were identified that would result in a downgrade
in classification of the growing areas. However, surface water drainages in association
with agricultural practices and other non-point sources of pollution will require further
evaluation and sampling.
The drainage system located along Marrowstone Island provides fifteen direct or indirect
points of discharge into Kilisut Harbor and Mystery Bay. Because of their vicinity to
small agricultural practices, the Department should periodically sample the discharge
from drainages D7, D10, D11, and D21. Furthermore, the Department should evaluate
the natural drainage originating through drainage sites D13 and D14 and sample the
runoff before it enters Kilisut Harbor below Smith Road. Wet weather sampling of these
discharges will be conducted by the Department in FalllWinter 2000.
None of the 129 on-site sewage systems evaluated were observed to provide a direct or
indirect discharge to the growing areas. Fifteen systems were classified as "potential
sources" because of their proximity to surface water and/or type of system evaluated in
association with the soils commonly located in this area. The soil type in the vicinity of
the on-site sewage disposal systems on Marrowstone Island provides only 24-40 inches
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of soil on top of an impermeable sandstone layer. This condition can result in an indirect
discharge of improperly treated sewage to the growing area.
The moorage of vessels in Mystery Bay is an issue of increasing importance to the
Department. The number of vessels moored in the bay at this time will not result in an
increase of the shellfish closure zone around Mystery Bay State Park. However,
Department communication to Jefferson County has stated that an increase in the
moorage in the bay may result in an increased closure area. The Department should
continue to document the number of moored vessels in this bay during routine marine
water sampling events. The Department should also coordinate with Jefferson County
and the Department of Natural Resources in an effort to evaluate the placement of
additional moorage within the Bay, as necessary.
Indian Island contains four waste disposal sites in the vicinity of the Kilisut Harbor
shellfish growing area. According to the Navy, these sites do not pose any public health
threat to the neighboring area and none of these sites are believed to impact the
shellfish harvesting locations. Site 10 and Site 34 are currently undergoing additional
evaluation activities. The Navy has conducted additional landfill closure activities (Le.
geomembrane cap and passive methane collection and discharge) to help alleviate the
introduction of surface water into this landfill. Site 10 does not have a bottom liner or
leachate collection and may be influenced by groundwater and tidal action. The Navy
has established a shellfish closure zone around Site 10 that does not allow the
commercial or recreational harvest of shellfish. The Department should place the Navy-
defined closure zone around Site 10 on the growing area maps. Due to its proximity to
Site 10 and the seal population using Rat Island, as defined in past Department
decisions, the Department should not allow any commercial or recreational shellfish
harvesting activities to occur on Rat Island. The A TSDR report indicates that
contaminants do exist in the vicinity of Site 34, however, ground and surface water are
not impacted. The Department should continually evaluate the remediation activities,
performed by the Navy, occurring in the vicinity of Kilisut Harbor.
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Kilisut Harbor I Mystery Bay Shoreline Survey
APPENDIX A
Drainage Evaluation
Site # Location Comments
01 Lat. N 480 04.718' Indirect discharge >200 feet from Kilisut Harbor.
Long. W 1220 42.421'
02 Lat. N 480 04.273' Culvert crossing to east side of Flagler Street.
Long. W 1220 42.124'
03 Lat. N 480 04.022' Indirect discharge to Kilisut Harbor.
Long. W 1220 42.113'
04 Lat. N 480 03.602 At entrance to Mystery Bay State Park. Indirect
Long. W 122041.659' discharae to Mystery Bay.
05 Lat. N 480 03.469' Culvert across Flagler Street from Schwartz Road.
Long. W 1220 41.488'
06 Lat. N 480 03.408' Culvert across Flagler Street from East Beach
Long. W 1220 41.454' Road. Indirect discharge to Mystery Bay, >200 feet
to surface water.
07 Lat. N 48003.213' Direct discharge to Mystery Bay. Drains small hobby
Long. W 1220 41.387' farm. Next to SS.
08 Lat. N 48003.082' Direct discharge to Mystery Bay. Sign in drainage
Long. W 1220 41.466' "private beach keeo off".
09 Lat. N 480 03.050' Direct discharge to Mystery Bay. South side of
Long. W 1220 41.468' Nordland General Store.
010 Lat. N 48002.954' Direct discharge to Mystery Bay. Drains agricultural
Long. W 1220 41.470' area.
011 Lat. N 48002.917' Direct discharge to Mystery Bay. Drains agricultural
Long. W 1220 41.473' area.
012 Lat. N 48002.915' Culvert under private driveway. Direct discharge
Long. W 1220 41.495' from wetland to Mystery Bay.
013 Lat. N 48002.528' Field to field drainage under Griffiths Point Road.
Long. W 1220 41.536' Drainage filters through wetland area then to Kilisut
Harbor.
014 Lat. N 48002.531' Field to field drainage under Griffiths Point Road.
Long. W 1220 41.679' Drainage filters through wetland area then to Kilisut
Harbor,
015 Lat. N 480 02.525' Indirect discharge to Kilisut Harbor.
Long. W 122041.938'
016 Lat. N 480 02.562' Culvert across Griffiths Point Road to drainage
Long. W 122041.980' ditch.
017 Lat. N 480 02.674' Culvert across Griffith Point Road to culverted
Long, W 122042.039' drainage.
018 Lat. N 48003.191' Culvert across Griffiths Point Road.
Long. W 122041.710'
019 Lat. N 48003.217' Culvert across Griffiths Point Road, may be indirect
Long. W 1220 41.764' discharae to Mystery Bay.
020 Lat. N 480 02. 157' Culvert across Flagler Road to field, approximately
Long. W 122041.488' 1,000 feet to Kilisut Harbor.
021 Lat. N 48001.815' Indirect discharae, approximatelv 50 feet to Kilisut
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Lon
Lat.
Lon
Lat.
Lon
W 1220 41.388'
N 480 01.695'
W 1220 41.525'
N 48001.571'
W 1220 41.646'
Harbor.
Direct discharge to Kilisut Harbor. Approximately
25-foot hi h bank dischar e.
Indirect discharge approximately 100 feet to Kilisut
Harbor.
17
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