HomeMy WebLinkAboutBristol Bay Regional Power Plan Newhalen River 1983 Juvenile Sockeye Salmon Studies 1983y y
Contract No. CC-08-21 08
BRISTOL BAY REGIONAL POWER PLAN
NEWHALEN RIVER
1983 JUVENILE SOCKEYE SALMON STUDIES
October 1984
Prepared for
Alaska power Authorit Y
By
14007.1 7 -W(D)-1
PROPERTY OF:
Alas l c3. Po/vcr Authority
334 W. 5th A'ie.
Anchorage, Alaska 99501
Stone &. Webster Engineering Corporation
Denver, Co lorado
TARLE OF CONTENTS
APPENDICES -~IEWHAU~N RIVER (RM 13), SPRIf\JG 1983
Catches By All Gear Types
2 Lenqth-Frequency of Sockeye Fry and Smolt
3 Sockeye Smol t Length and Weiqht Data
4 Newhalen River Air and Water Temperature
ii
Number
L TST OF FIGURES
The Kvichak River System Showing the Location of
"lewhalen RM-7, RM-13 and RM-22 Study Sites
2 Cross-Section of RM 13, Newhalen River, With Station
Locations Under Two Flow Conditions, 1983
3 Overview of RM 13 Site Showinq Gear and Station Locations,
1983
4 Angled Screen Flume Arrangement
5 Plan View of Flume Wi th Impingement Test Chamber Inserted
6 Flume Cross-Sectional Velocity Distribution Upstream of
Angled Screen
7 Velocity Distribution Along Angled Screen at Approach
Velocity of 0.6 Feet Per Second
8 Cross-Section River Velocities, "Iewhalen River,
RM 13, 1983
9
10
Da ily 9x9 Foot Ne t Smolt Catches, Section 4,
Newhalen River (RM 13), 1983
Da ily Inclined PI ane Trap Fry r:atches,
Newhalen River (RM 13), 1983
II Selected Scales (X 34) of Newh81en River
Sockeye Smolt, RM 13, 1983
12 Sockeye Smolt Age -Lenath Relationships, RM 13,
Newhalen River, 1983
iii
5
8
15
If)
18
19
22
25
27
31
Numher
2
L lST OF TABLES
Newhalen River (RM 22) .A.dult Sockeye
Escapement, 1983
Summary of Fry Impingement Duration Test Results
iv
Paqe
37
1.0 INTRODUCTION
As part of the Bristol Bay Regional Power Plan Study, the Alaska Power
Authority is investigating the feasibility of a hydropower development on the
Newhalen River near Iliamna, Alaska. A preliminary description of the proposed
Newhalen River Hydroelectric Project is contained in the Bristol Bay Regional Power
Plan Interim Feasibility Assessment (Stone & Webster 1982). The project would entail
the diversion of water into a canal at river mile (RM) 7 for conveyance to a
powerhouse near the mouth of the Newhalen River.
On the basis of a proposal by Dames & Moore, Stone & Webster was authorized
by the Power Authori ty to complete a second year of baseline studies on the Newhalen
River. The 1983 studies completed at river mile (RM) 13 complement those completed
by Dames & Moore at RM 7 in 1982 (Dames & Moore 1982). The evaluations focused
on temporal distrbution and enumeration of sockeye salmon (Onchorhynchus nerka)
smolt and fry.
Dames & Moore under contract to Stone & Webster had complete responsibility
for 1982 field work and data analysis. As in 1982, Dames & Moore worked
cooperatively with Patrick Poe of Fisheries Research Institute (FRY), University of
Washington. Mr. Poe assisted in sample site selection, timing of sampling,
mobilization, and sampling.
There were several differences between the 1982 and 1983 study procedures and
designs other than the change in sampling location. The 1982 study was designed
primarily to sample spacial and temporal distribution of smolt and fry. After
beginning the study, Dames & Moore was requested to collect data on the numbers of
outmigrants, and as noted in their 1982 report (Dame & Moore 1982), the sampling
program had limitations concerning the accuracy of this effort. Changes were made in
the 1983 program study methods so that both spacial and temporal distribution and
number of outmigrants could be adequately sampled. An additional request was made
for conducting adult sockeye counts after this sampling effort began. The adult field
effort was completed totally by FRI under contract to Dames & Moore.
1
Another feature of the 1983 study was the inclusion of limited fish diversion ,mrl
impingement survival tests conducted in the Newhalen River by Edward P. Taft of
Stone & Webster. These studies were undertaken to obtain preliminary information on
the potential effectiveness of a fish protection system at the canal intake to the
hydroelectric plant.
2
2.0 ACKNOWLEDGEMENTS
Financial support by the Alaska Power Authority made this study possible.
Dames & Moore coordinated the field program and prepared the draft report. Stone &
Webster added information relative to the fish diversion and impingement survival
studies and oversaw the project effort.
As in 1982, FRI provided both personnel and an extensive equipment base in the
Iliamna vicinity which allowed the project to be completed. Patrick Poe and Warner
Lew provided a great deal of energy and expert ise to the field program. FRI part ially
supported the program by allowing use of numerous gear types (boats, tanks, etc.) at
no charge to the Power Authori ty.
Eastside Net Shop (Bothell, Washington) again provided large wingless fyke nets
of special design on very short notice. Trans Alaska Helicopters Inc. (helicopter
charter) and Iliamna Air Taxi (room, board, and fixed-wing plane service) provided
excellent service as in 1982.
A special thanks is owed to two individuals. Dick Parent, Dames & Moore field
engineer, provided his ingenuity in the mobilization and demobilization of sampling
gear and camp facilities. Ward Johnson, FRI graduate student, assisted in scale
reading and data evaluation leading to outmigration estimates. The cooperation
received from the residents of the Nondalton, Newhalen, and Iliamna areas is also
greatly appreciated.
Finally, the spring field crew which gracefully put up with poor working hours
and conditions for up to 7 weeks included William Blaylock, Dave Erickson, Ronn
Griffin, John Isakson, Warner Lew, Dick Parent, and Patrick Poe. Various FRI staff
members crewed the RM 22 adult counting station in 1983, and are also to be thanked
for their contribution.
3
3.0 MATERIALS AND METHODS
3.1 SPRING METHODS
The 1983 sampling goal was to begin sampling before the 1982 start date
(May 10). Verbal notice to proceed in 1983 was received on May 3. A
biologist and field engineer departed for Iliamna to begin preparation
on May 5. The major portion of the freight, helicopter support, and three
additional biologists arrived in Iliamna on May 9 to initiate full camp
mobilization. The first outmigrant sampling started on t·1ay 11. The field
program was terminated after 7 weeks (June 25).
With fund ing reduced from 1982, a site less remote than RM 7 had to
be selected in 1983. A major cost saving could be made if helicopter
involvement was reduced. Therefore, the 1983 site had to be upriver of
Rt~ 7 and near the haul road between Iliamna/Newhalen and the landing on
the l'Jewhalen River which leads to Nondalton. The site selected on May 9
and 10 under relatively low water flows was about hal f way between Bear
and Lover's creeks at about RM 13 (Figure 1). This site had shallow
enough water depths (to six feet) to accommodate the anticipated increase
in water level to still allow our 9x9-foot net frames to fish later in
the spring.
3.1.1 Net and Trap Sampling
As in 1982, the Newhalen River proved to be a very dynamic system in
terms of river flow. Initial flows in early tvlay were about 5,000 cfs and
these increased to about 15,000 c fs toward the end 0 f June. A cross sect ion
of the RM 13 site and two measured flow levels in t;lay and June is shown in
Figure 2. Also noted are the locations 0 f the six sampling stations sel-
ected along the transect. As in 1982, RM 13 bottom conditions, consisting
of large boulders, determined to a great extent, station location. Equal
spacing of stations, due to bottom conditions across the river, was not
possible.
4
t ....
l
FRI NEWHALEN RM 22
ENUMERATION SITE
NEWHALEN RM 13
STUDY SITE, 1983
KILO.,..,.,..
X 5
10
10 20
MILia
SOURCE: Modified from FRI unpublished report.
Job No. 12023-013-20 5
The Kvichak River System Showing
the Location of Newhalen RM-7,
RM-13 and RM-22 Study Sites
Dames & Moore
Figure 1
o
~ 5
l.J...
Tower
6/20/83 USGS 4.37' OR 13,080 cfs
5/16/83 USGS 2.30' OR 5,780 cfs .t· l------.:.......-~------------~ .. : .
. -.':
.w •
... ~·t ••
•• -,..,.-."!'~~ ~;: ... : .. : : ... :. : ::: • .:::. :::i:::·:··
.... ,~:.: .. ..... --~~~~ ..... .
. : ::: .. :-.' ::: ,. :, .. : .. ::.'i:-:':'
E A S T
BAN K
STATION NO.1 2 3 4 5 6
400 350 300 250 200 150 100 50 o
Distance from East Bank (Ft)
Cross-section of R M 1 3 •
Newhalen River, with Station Locations
under Two Flow Conditions, 1983
Dames & Moore
Job No. 12023-013-20 6 Figure 2
Based upon 1982 experience, the net and trap sampling program was
redesigned to attempt greater success at fry and smolt enumeration. The
major changes were larger wingless fyke nets (9x9-foot) and two cables
across the river to concurrently deploy them. One net was stationary while
the other was moved to one of five remaining stations (see Figure 3).
Bridal lengths on the upstream cable were made long enough to allow the two
nets to fish about at the same position in the river.
The larger new nets were 29 feet long with the 9x9-foot opening tapered
to a 6-inch collar which lead from a 7-foot piece of flexible hose and into a
floating live car. The progression of net mesh sizes (all stretch measure)
was from 1.5 inches at the front, 0.5 inch in the midsection, to 0.25 inch at
the cod end. With the exception of extra strengthening lines from frame to
collar, these nets were similar to standard FRI surface tow-nets. This type
of FRI gear is towed between two boats in lake studies.
The larger 9x9-foot nets, upon arrival May 20, replaced a 3x9-foot net
of 1/8-inch knotless nylon (0.25-inch stretch) used last year and in the
first LJ. days of sampling in 1983. -The sampling schedule with the two large
cabled fyke nets was finall y set as follows. The downstream cable (net was
designated 9x9D) fished at a fixed position initially selected at Station 4
(Figure 3). This station existed from t~ay 20 to June 5 when an east bank
tree failed and the fixed cable collapsed. In mov ing to a new tree support,
the fixed downstream station moved to the west about 30 feet at what might be
labled Station "3.5" where the downstream net operated from June 6 through
June 22. The upstream cable was initially used to fish all six stations to
locate areas of smolt abundance in the river cross section. From May 24 to
June 13 the upstream cable was operated in concert with the downstream cable
ann fished the same parts of hours as much as possible. In 1983, the
9x9-foot frames collapsed on three occasions.
In 1982 the single cabled net \-Jas often moved each hour (Dames &
rloore 1982). In 1983, with two cables, the upstream-cabled (mobile) net
was usually moved once each sampling period with a focus from 9 p.m. to
4 a.m. each nioht. The sampl ing program with a fixed net and a net moved
7
Trees
'.' :~ .:
' . . '
.'
V 3 X 3 W
River Flow
t Upstream
Cabl e
Trees
Downstream
Cable Index
Station 4
4 X 4 E V
W EST
BAN K :.
,": .
. '
' . . ' ' . . "
'. ::.
-.: .;
D
IPT
Note: Net on upstream cable shown on
fishing station 5; index net
is shown on station 4. Dotted
outline of net shows approxi-
mate net location after 6/5/83.
Not to scale.
.'.
" ~: . .:.
E A S T
BAN K
Overview of RM 13 Site Showing
Gear and Station Locations, 1983
Dames & Moore
Job NO.12023-013-20 8 Figure 3
each sampling period prov ided numbers of smolt and fry caught that could
more accurately be expanded to an outmigration estimate.
Other gear types used in 1982 were aqain used in 1983 and included
the float ing inclined plane trap (IpT) and two smaller wingless-fyke nets
Ox3-foot and 4x4-foot openings) of 1/8-inch knotless nylon (0.25-inch
stretch) . For a more complete description of these gear types see Dames
& Ho 0 r e (1 982) .
The six sampling stations (numbered 6 to 1, east to west banks) along
the cables crossing the river were 88, 150, 200, 250 290, and 320 feet,
respectively, from the center of the east bank tower (Figure 3). There
\'iere about 20 feet between the center of the tower to the east bank itself.
Stations and 6 were sampled few times since preliminary 3x9-foot
net catches and shore fyke nets near these locat ions caught few smolt and
fry in 1983. The bulk of the mobile (upriver-cable) 9x9-foot net sets
were at Stations 2, 3, and 5, while the fixed (downriver cable) net fished at
Station 4 until gear failure on June 5 moved it to about Station 3.5.
As in 1982, the mobile net system was fished most often in the period
from 9 p.m. to 4 a.m. each night. Net handling in this period revolved
around sets each hour and set durations usually involved an hour, 30 minutes,
or 15 minutes, with the determining factor being the anticipated abundance of
smolt and/or fry. Sampling times were reduced to intercept fewer juvenile
fish during anticipated high abundance hours.
Shore-mounted fyke nets--4x4-foot on the east bank and a 3x3-foot on
the west or camp bank--were fished as in 1982. The onl y movement was to
slowly bring the net closer to shore as the river rose in elevation (Figure
3) . Generall y the nets we re kept in shore positions in about 2.5 feet 0 f
water. Both nets had floating live cars to reduce fish Mortality. See
further descriptions of the gear in Dames & Moore (1982).
9
The inclined plane trap (IPT) was placed downriver about 300 yards
from the RM 13 cables and fyke nets (Figure 3). The trap was located in
mid-channel with anchors.
on the IPT used.
See Dames & Moore (1982) for further details
To summarize, the following gear types and locations were fished in
the spring 1983 studies at RM 13:
Number of
Gear Type Dates Fished Observations*
9x9-foot upstream net 5/20/83 to 6/13/83 174
9x9-foot downstream net 5/24/83 to 6/22/83 206
3x9-foot net 5/16/83 to 5/26/83 58
3x3-foot net (3x3 W) 5/13/83 to 5/21/83 238
4x4-foot net ( 4x4 E) 5/11/83 to 6/20/83 198
Inclined plane trap 5/16/83 to 6/22/83 276
*Times between observations ranged from minutes (between hour sets) to
multiple hours depending upon gear type, concentrations of smolt or fry
in the river, and gear availability.
As in 1982, several parameters in addition to catch data for all
species (including incidental resident fish) were recorded during index
hours and throughout the day, as possible. These parameters included:
(1) water and air temperatures (mean, minimum, and maximum every 4 hours
in Data Pods-Model DP2321), (2) water level on a loaned USGS staff gage, and
(3) general weather conditions. In 1983 a recording pyrheliometer (24-hour
clock) was operated at RM 13 from May 16 through June 18.
Fish processing consisted of species separation and counting with
selected sockeye subsamples taken for length-frequency measurements. As
requested by Alaska Department of Fish and Game (ADF&G), scale samples with
length and weight measurements were taken from selected sockeye smolt at
varying times during their outmigration. Scales were field-mounted on
slides. Fry and smolt subsamples were preserved in buffered 10 percent
formalin for possible future evaluation of smolt otoliths and other
parameters.
10
3.2 SUMMER METHODS
As in 1982, a field camp at RM 22 on the Newhalen River was established
as the RM 13 camp was demobilized. In 1983 these facilities were operated
in much the same way as in 1982 (Dames & Moore 1982) with the exception being
only one inclined plane trap was operated about 100 to 125 feet from the east
bank in a deep channel at this river cross section (see Figure 5 in Dames &
Moore 1982). IPT operation was as described for 1982. More details of the
adult counting operation by FRI can be found in Poe et a1. 1983. Basically,
lo-minute counts were made on each hour from each shore as conditions
permitted.
3.3 SPRING ANALYTICAL PROCEDURES (NETS AND TRAPS)
The procedures described in 1982 studies (Dames & Moore 1982) were
again used to extrapolate and interpolate data on fry and smolt catches
to both estimate an outmigration and define the horizontal distribution
of these juvenile sockeye salmon.
One major difference, however, existed in the data available to do
these analyses. This was the existence, for most of the spring, of con-
current 9x9-foot net catches both at an index station (initially Station 4)
on the downstream cable and at varied stations on the upstream cable (usually
Stations 2, 3, or 5; Figure 3). The catch data expansions were therefore
completed with a more accurate representation of the relationships of the
four main river stations to one another than in 1982. Stations 1 and 6 were
seldom fished due to low fish catches there.
In 1983 the mobile net was left through the peak migration hours
(9 p.m. to 4 a.m.) at a single station while the index station was also
fishing. In 1982 the single mobile net moved each hour to different stations
dur ing some days and was left on the RM 7 index ing station for the ent ire
night on other days.
11
3.4 SUMMER ANALYTICAL PROCEDURES
Due to the few fry caught in the IPT at RM 22 during the adult counting,
no evaluation procedures were required for sockeye juveniles.
Adult sockeye counts (10 minutes, each bank, each hour when possible)
were expanded by multiplying both bank counts by 6 and adding them for each
24-hour day. Data expansion procedures are described in Poe et a1. 1983.
3.5 GEAR LIMITATIONS
As in 1982 (Dames & Moore 1982), similar gear limitations existed in
1983 with a few exceptions. The larger 9x9-foot nets most likely had less
net avoidance by smolt and fr y because of the bigger net openings than in
1982 Ox9-and 4x8-foot nets). In addition, green dyed net web was used
in 1983 I'lhe reas the net web was wh i te in 1982.
Smolt most likely escaped capture on occasion even in these 9x9-foot
nets as well as the 3x3-and 4x4-foot shore nets under lower velocity
conditions at shore stations and to a lesser degree at Stations and 6.
Fry were probably unable to swim out of these nets at even these "lower"
velocities.
On the other hand, smolt probably did not pass throuClh the net web in
any nets while fry likely did escape capture in this manner. As the 1983
field season progressed, the 9x9-foot nets sagged in the cod ends, allowing
bulges to occur in the net web just in front of the collar leading to the
flexible 6-inch pipe. This also occurred in 1982. With a more distinct net
bulge, along with higher velocities as the spring season progressed, some fry
passed through the net and not into the live car where they could be counted.
The percent age lost is not known, but 1 ikel y increased through the field
season.
The net catches must therefore be considered a minimum that passed
that water column in the sampling period since some smolt avoided or escaped
12
the nets and some fry passed thro~gh the net web under some conditions.
Other losses occurred when live cars occasionally flooded.
Another limitation were the longer 9x9-foot net bridles coming from the
higher cables over the river in 1983 as compared to 1982. The increased
bridle lengths in 1983 increased net set and retrieval times and most likely
reduced the accuracy of the 1-hour sets. These sets were in most cases 50-
to 55-minute sets since the attempt was to set on consecutive hours from 9
p.m. to 3 or 4 a.m. This error in 1-hour sets was not corrected for because
of the variability in the net haul times between stations. In calling a 50-
to 55-minute set with additional varied set retrieve times (when the net is
still fishing to some degree) a 1-hour set, we have slight! y underestimated
the numbers of fish actually passing the station in that 1 hour.
This time error was less of a problem in 30-and 15-minute sets where
there was sufficient time in consecutive hours to operate the net. However,
even in these cases, the net can be fishing although inefficiently in both
the set and retrieval process. In these shorter sets we can be overesti-
mating the fish that passed that net station in the set time (15 or 30
minutes). \vith a mixture of "1-hour" and 15-or 3D-minute sets, the
underestimates and overestimates may to some degree offset one another.
Varying river debris loads during the sampling period also influ-
enced net and trap efficiencies to an unknown degree through the spring
program in 1983.
13
3.6 FISH DIVERSION At'--ID IMPII'JGEMEt'--IT SURVIVAL STUDIES
Si nce the Newhalen River maintains a large run of sockeye salmon, concern has
been expressed over the potential losses of outmigrants (fry and smolts) as a result of
passage through the project. Consequently, preliminary eV8luations of project
feasibility have considered means to intercept fry and smolts entering the canal ann
safely returning them to the river. A comhined fish diversion 8nd collection system
has been suggested, using angled, traveling water screens.
In order to obtain preliminary information on the potential effectiveness of the
fish protection system, a series of fish diversion and impingement survival studies was
conducted in June of 1983 on the Newhalen River at RM 13.
The fish diversion and impingement surviv81 studies were conducted in a
4x4x8-foot test flume. This flume was usee! for both diversion and impinqement tests.
For diversion testing, an insertable screen panel was fabricated (Figure 4). The p8nel
incorporated 2.0-mm plastic mesh 8S the diversion medium. The panel frame was
nesiqned to fit into the flume at a 250 angle to the approach flow with aCCLIrAte
alignment of the downstream end of the frame to a stationary bypass wall. The bypass
was six-inches wide, full depth and two-feet long and discharged directly to the river.
At the upstream end of the flume, a 5.0-mm mesh inflow screen was pl8ced
across the flume entrance to contain test fish within the flume Rnd to hlock the
passage of larger debris.
For impingement tests, the diversion panel ann inflow screen were removed and
a segmented box was inserted across the width of the flume. The four segments were
about one-foot wide and incorporated 0.5-, 0.5-, 1.0-ann 2.IJ-mrn plastic mesh,
respect ivel y (Figure 5). Testi ng was conducted wi th the 1.0-mm and 2.0-mm meshes
only. A 5.0-mm plastic mesh was attached to the front of the entire box which
contained the test fry within the appropriate segment.
14
~----------------------------------------------------------------------~=
Flow
5mm Inflow Screen\ ' f
2mm Angled Screen
I I
I
6" Wide Bypass
NEWHALEN RIVER
Angled Screen Flume Arrangement (Plan)
15 Figure 4
co ... • '" co
0(
~------------------------------------------------------------------------,~
(
Impingement Test
Chamber Insert
(
-FlOW
~ Smm Retention Screen • ------------,.\
I
~ • F2.0mm :f.9m.rn~ ~Q~§rn_rn
............ At ................................ ,. ....................................................... '"
Plan View of Flume with Impingement
Test Chamber Inserted
16 Figure S
o
~ • ... o
c(
For all testing, the flume was submerqed in the river near the shoreline to a
depth of about I B-inches. Given available river flows at the selected location, a mean
cross-sectional velocity of about 2.2 feet per second was achievable with the anqleri
screen in the flume (Figure 6). Locating the flume in a higher velocity area was not
deemen desirable for these preliminary studies due to the difficulty in securinq it
firmly with available anchoring devices. The selected location also resulted in
relatively uniform flow conditions, as shown on Figure 7.
All test fish were supplied by Dames & Moore and were collected at the flume
site with the 9x9-foot fyke nets (smolt) and the inclined plane trap (fry) descrihed
previously. Fish were generally tested within one nay of capture. Prior to testinq,
they were held in tanks (smolt) or a netted box (fry) submerged in the river.
Testing of the angled screens was conducted with both fry and smolt. Since
smolt were capable of swimming easily against the maximum velocity achievable in
the flume (approximately 1.1 feet per second), all tests were conducted at this
velocity. Fry, on the other hand, displayed little ability to guine alonq the screen <It
this velocity and were, therefore, tested at approach velocities as low as 0.5 feet per
second.
Few smolt were available for anoled screen testing. Further, the fish were
obviously capable of maintaining their position in the flume at the velocities tested
and easi Iy avoided impingement on the screen. Therefore, for these preliminary
studies, efforts were concentrated on observing behavior for input to future studies
rather than gathering extensive quantitative data.
Unlike smolt, fry Flppeared to have difficulty diverting on the screen <It a low
velocity. In general, more than 50 percent of the fry impinoed immediately upon
release while the others diverted to the bypass. Eventually, the impinged fish worked
their way along the screen and bypassen, usually within several minutes. It appeared
that the fry had the ability to orient into the current and swim against relatively high
velocities. However, they did not react as strongly to the screen as might have been
expected. Since fry impingement rates were high, and the need for a collection-type
of screen was evident for this life stage, diversion testing aq<lin concentrated on
observing behavior rather than collecting quantitative elata.
17
~--------------------------------------------------------------------~. -
18" -1.05 1.05
+ +
1.05 1.10
10" -+ +
1.00 1.05
4" + +
-I I
6" 12"
V ""T' Water Depth
T 1.00 1.10 1.10 = 20"
+ + +
1.07 1.10 1.10
+ + +
1.00 0.97 1.10
+ + +
I
<i 12" 6"
Flume Cross-Sectional Velocity (Feet Per Second)
Distribution Upstream of Angled Screen
18 Figure 6
co ... • ... co
0(
~------------------------------------------------------------------------------------------~:
0.65
+
0.60
+
0.6 __ ..................... ,
+ ........................ , ........... ,. ......................... ,. .. ~;
o~~~
0.6~
+
I 0.55
1-"' ................... 0.60~ +.:, ~. Flow :: ~ : : ::: + .....
0.7
+
0.80
-± 0.60::";'; =-: ;
.,.. •• ,.,.+J .......... '-••.•. + ................. ,t" .... ~
Velocity Distribution Along Angled Screen at
Approach Velocity of 0.6 Feet Per Second
(Measurements Taken at Mid-Depth)
19 Figure 7
o ... • ... o
0(
As previously staten, impingement survival tests were conducted wi th 1.0-ann
2.0-mm meshes. Although little was known about the survival potential of sockeye
fry, it was believed that they would be relatively hardy. Therefore, early tests were
conducted for impingement durations of eight and 16 minutes. Since these durations
initially resulted in low mortality, all further tests were conducted similarly. Every
attempt was made to maintai n the highest possible velocity through the test screen
panels. However, velocities generally decreased Slightly over the duration of the test
due to debris clogging. Velocities at the beginning of each test ranged from 1.2 to 1.5
feet per second; by the completion of a test, the velocity had decreased by no more
than 0.2 feet per second.
At the time of each impingement test, two lots of about twenty fry were placen
ina release container. The test screens were cleared of debris and a rubber mat was
placed across the front of the two test chambers to stop the flow. The fish were then
released into the \.0-and 2.0-mm screen segments and the rubber mat was
immeniately removed causing the fry to impinqe across the surface of the two
meshes. After the desired test duration, the mat was agai n placed across the test area
to restrict the flow. Fry were observed immediately for siqns of stress or injury and
were then removed to a holding area for observation of latent (48 hours) survival.
For each day's experiments, a control group of fry was held for comparison of 48
hour mortality with the test fish. The controls were treated in exactly the same
manner as the test fish but were not subjected to impingment.
The holding facility consisted of a flow-through water bath in which 4-inch
diameter holding cups with mesh-covered bottoms were placed to hold test and control
fry. Each group of about twenty test or control fish was split equally between two
cups to avoid crowding. Initial mortality observations were mane one hour after
each test. This short delay allowed stunned fish to recover or die. Thereafter,
morUdity was recorded at 6, 12,24 and 48 hours. After 48 hours, all remaininq live
fish were enumerated and returned to the river.
20
4.0 RESULTS AND DISCUSSION
4.1 SPRING STUDIES
In the period from May 11 to June 22, 1983, Dames & Moore, assisted
by FRI, completed over 1,150 observations of sockeye smolt and fry catches
from the nets and trap fished at RM 13. In this period, over 23,000 smolt
and over 100,000 fry were captured and enumerated. Fork length on several
thousand of these smolt and fry was measured and recorded and over 200 smolt
were processed for scales, length, and weight. Several hundred smolt and fry
were labeled and preserved. All scale, smolt, and fry samples are available
to ADF&G from FR I.
In 1983, as in 1982 (Dames & Moore 1982), a great deal more anal yses
are possible with the available data set. Therefore, all pertinent data
collected are appended to this report. Appendix Tables 1 and 2 present
the raw data used in these anal yses. As per the request of ADF&G, Appendix
Table 3 prov ides the sockeye smolt length and weight data for the slide-
mounted scales taken in 1983. Appendix Table 4 provides air and water
temperature data for several Newhalen River locations. The 24-hour
pyroheliometer strip charts for the period May 16 through June 18, 1983
could not be reproduced.
request.
The original charts are avaliable from FRI upon
As in 1982 and shown on Figure 2, the Newhalen River again underwent
dramatic flow increases in 1983. The cross-sec tional velocity profiles
at RM 13 for two flow levels are shown in Figure 8. All velocities were
measured about foot under the water's sur face. Increasing day length
and generally increasing air and water temperatures also occurred throuqh
the 7-week spring period.
4.1.1 Spacial Distribution
Smolt: While no specific study was directed at smolt vertical
distribution, a dramatic difference between 1983 and 1982 was seen in
smolt occurrence in the upper 18 inches at the river's surface. In 1982
21
8
"'0 c: 7
0 u 6 OJ
V1 ...... 5 -l->
OJ
OJ
l.J... 4
>, 3 -l->
U 2 0 .-
OJ
> 1
0
400 350
Job No. 12023-013-20
300
June 20, 1983
........ . ...... . ..... .-. .... ..-.... e.-...•.••.. _ _ ..
\'May 16, 1983 •.•••...••.•••
250 200 150 100
... · · · ........
50
. ....
o
Distance from East Bank Tower (Feet)
Cross-section River Velocities.
Newhalen River, RM 13, 1983
Dames & Moore
22 Figure 8
.....
-
-
-
-
....
-
-
at Rt~ 7, large numbers 0 f smolt were taken in the IPT which fishes these
surface waters. In 1983, at RM 13, almost no smolt were taken with the
IPT. Many factors could contribute to this vertical distribution chanqe
including the different sampling site, dominance of 1+ smolt in 1982 and
2+ smolt in 1983, density of smolt, etc. Of interest are the unconfirmed
reports from the Kvichak River acoustic site that smolt were deeper in
the water column in 1983 than in prior years.
The horizontal distribution of smolt at RM 13 was much less distinct
than at RM 7 in 1982. This is possibly due to age and abundance of smolt
as well as the less distinct channel and the pattern of river water
velocities at RM 13 in 1983 (see Figure 8). This may also be due to a
better definition of smolt distribution in 1983 as compared to 1982. As
part of the smolt outmigration enumeration (Section 4.1.3), the followinq
relationship between stations was summarized for the entire spring period:
Station:
Smolt
relationship
to index
West Bank
o o
2 3 4
0.106 0.564 1.0
5 6 East Bank
0.324 o o
Inconsequential numbers of smolt were taken on and near shore.
no percentage amount of smolt were assigned there.
Thus,
At RM 7 in 1982 with many more 1+ than 2+ smolt (reversed in 1983) and
under different site and velocity conditions, almost 90 percent of the smolt
were estimated to have passed through the horizontal area represented by a
sinale midriver station (Number 2).
Fry: The vertical distribution of fry was seen by comparing IPT and
9x9-foot net catches. As in 1982 the fry appear more numerous in the
upper 18 inches of water fished by the IPT with the disproportionate catch to
area sampled. A 9x9-foot net, fishing an average of six feet deep, samples
about 7,776 square inches of water while the 18x30-inch IPT opening samples
about 540 square inches of surface water or about seven percent of the
23
+-'
0
E
Vl
4-
0
~
(])
.0
E
:::l
Z
14000~---------------------------------------------'
12000
10000
8000
6000
4000
2000
*
15
Mean River Flow
0
0
0 ........
x
10 <11
4-
U
3:
0
L.J....
~
(])
> 0,....
~
5
* (])
~
:::l
,.-
co co
4-+-' co
"
Based upon station 3 catches
Daily 9 x 9 Foot Net Smolt Catches,
Station 4, Newhalen River (RM 13), 1983
Dames & Moore
Job No.12023-013-20 25 Figure 9
smolt catch began the season. In 1983 (Figure if) the third net catch at
the index station (Station 4) was the largest achieved. With this pattern of
occurrence by catches at Station 4, it appears that smolt had started their
movement from the Newhalen River system about the same time as in 1982. If
the large peak in 1983 was the maximum smolt appearance, this is quite close
to the same date that smolt peaked more gradually in 1982.
Ear lier net catches with 3x9-foot nets (May 16 to 20) did not capture
large numbers of smolt, possibly indicating the May 23-26 and June 1-2 peaks
in Figure 9 were irregular occurrences rather than the end of a multi-day
peak in smolt movement. Unfortunately, our goal in 1983 of starting sooner
was not met. Hopefully an earlier field season can occur in a future year.
Another smolt difference is the multi-day pattern of smolt occurrence in
1982 versus the more sporadic appearance of smolt in 1983. This may be due
to the smolt abundance/age differences, the closer proximity to different
sources of smolt in 1983, and the different site characteristics between RM 7
and 13.
The disturbing situation in this smolt temporal distribution is that
smolt in large numbers could have been moving prior to the initiation of
sampling. If this is the case, smolt escapement estimates are likely
conservative with fish missed before RM 13 sampling was operational.
Fry: The temporal distribution of so~keye fry in 1983 (Figure 10)
was much like that in 1982. Fry peaked at about the same time in each
year--June 7 to 12. The fry catch curve in 1983 (Figure 10) did not seem as
closely timed to river flows as in 1982 although there still appears to be an
association. Fry movements in the Newhalen River may be more associated with
day lengths than previously thought on the basis of the 1982 (RN 7) study. A
different type of water year with river flows out of the 1982 or 1983 pattern
I"lould be required to determine whether flows or day length are dominant
factors in fry movement.
26
4000~-----------------------------------------------------r20
3000
>,
!...
L1-
4-
0 2000 Mean River Flow
!...
OJ
..0
E
::::l
Z
1000
Job No.12023-013-20 27
9 10 11 12 13 14 15 16 17 18 192021 22
June
15
10
5
Daily Inclined Plane Trap Fry Catches,
Newhalen River (RM 13), 1983
,
0' o·
0
...-t
X
1.11
4-
U
3:
0 ,.....
L1-
!...
OJ
>
0:::
Dames & Moore
Figure 10
4.1.3 Enumeration
Smolt: The estimated number of sockeye smolt passing RM 13 from
May 20 to June 19 in 1983 was 330,000, based upon a catch 0 f over 17,000
smolt at the index station. Additional smolt were captured at other stations
and a few smol t were taken in the IPT and shore nets. The one night I s set
with the 9x9-foot net on May 24/25 captured 70 percent of the smolt taken in
the entire 1982 program with 4x8-and 3x9-foot nets at RM 7. The sampling
program was better designed to achieve an outmigration estimate in 1983 and
had more efficient nets than 1982. This 1983 smolt value is conservative
since smolt were moving before and after this index period. The 1982 esti-
mates may have been underestimated because of the single net sampling program
and the smaller net openings.
In reaching these extrapolated catches from the index areas a large
potential source of error in this enumeration was seen. An inconsistent
relationship was seen between the index station (originally at Station 4) and
the other stations, especially 2,3, and 5. The 1983 smolt were nearly all
2+ fish whereas most smolt in 1982 were smaller 1+ fish. Smolt were more
horizontally spread in 1983 at RM 13 than at RM 7 in 1982 (see Section
4.1.1). Possibly some of these factors explain the inconsistent relationship
of the index station to the other stations. Closer proximity to the sources
of smolt at RM 13 in 1983 than at RI"1 7 might also be a factor in how hori-
zontally distributed smolt are at the two sample sites.
Another enumeration problem occurred on June 5 when a tree gave way
on the downstream cable with the index station. When reset that day, the
index station moved about 30 feet to the west to become about Station
3.5. To an unknown degree, the consistency of the "index" station was
influenced.
The better data set Ivith 2 nets concurrently sampling in 1983 likely
shol'/s some details of the smolt distribution pattern that were not seen
in the simpler data set in 1982 at RM 7.
28
Too many variables exist to directly compare the 1982 and 1983
smol t numbers at the RM 13 and RM 7 sites. Due to the greater sampl ing
efficiencies in 1983, the 1983 smolt estimates are likely closer to true
outmigration escapements than the 1982 estimates from RM 7. The 1983 smolt
outmigration estimate is still conservative since smolt ran before and after
the index period. However, the errors existent in apportioning the smolt
numbers across the river in relation to a nonfixed index station could
contribute to over or underestimates.
Fry: The estimated number of fry passing Rr'-1 13 from May 16 to June 21
in 1983 was 1.3 million based upon the catch of over 47,000 fry in the index
st a tion net. More than 30,000 other fry were taken in the IPT and many
thousand more fry were enumerated in the other net station sets as well as in
the shore nets. The estimated passage at RM 13 ranged from under 1,000 to
over 130,000 fry per day in this index period. The bulk of the fry at RM 13
passed by in 12 to 14 days. The fact that most of a distributional curve
was seen indicates that no large numbers of fry were likely missed before
sampling began and after the sampling was completed.
As in the case of smolt, many variables exist that confound a comparison
of 1982 and 1983 fry outmigration estimates. The estimated adult escapement
to the Newhalen River system in 1981 and 1982 were about 250,000 and 215,000
respectively. However, some 64,000 of the 215,000 adults spawned in the
mainstem Newhalen River in 1982 as compared to 10,100 in 1981. The majority
of the production in the mainstem spawning area is above both RM 7 and RM 13.
The 1981 adult escapement produced an estimated outmigration of 7 million
fry, whereas the 1982 adult escapement produced an estimated outmigration of
1.3 million fry. This discrepancy of a disproportionate fry outmigration
from similar numbers of spawners has several possible explanations. First,
the 1982 fry outmigration may have been overestimated while that of 1983
may have been underestimated. Secondly, the fry surival may have been
considerably less from the 1982 spawning than that of 1981. However, other
factors may be involved. Six more miles of mainstem spawning went past RM 7
that were not seen at RM 13. This is not believed to be a major source of
error with the observed distribution of adults seen by FRI. Information on
29
the origins of fry in the 1982 and 1983 outmigrations is incomplete. Condi-
tions in the nursery areas of juvenile sockeye salmon in Lake Clark, Six-Mile
and Alexcy Lakes, may have been different enough to influence the duration of
residence before outmigration to Iliamna Lake. Therefore, it is possible
that a smaller portion of the production from the 1982 spawning, as compared
to that of 1981, migrated out of the Newhalen River system as fry and may
migrate later as age 1+ and 2+ smolts in 1984 and 1985.
The extrapolations made for the lost IPT in 1982 (Dames & Moore 1982)
could have caused over-or underestimates of the fry outmigration. The 1983
nets likely lost an increasing number of fry as the season (and associated
water veloc ities) progressed, causing an underestimate in 1983. This does
not appear to be a major factor since IPT and index net catch ratios remained
fairly constant through the 1983 sampling period.
4.1.4 Smolt Age-Lenqth Relationships
Some 184 of the 209 smolt scales samples taken in 1983 \~ere evaluated
for age at FRI. Figure 11 presents some representative scale photographs.
As noted earlier, 2+ smolt dominated the 1983 samples making selection of 1+
sized smol t easier than in 1982 when 1+ smolt dom inFted. The selection of
scales was mostl y from intermediate sized smolt to locate a break point in
age and length. Figure 12 presents the results of these evaluations. A
relatively sharp break exists at 97 to 98 mm with one scale overlap. This is
somewhat less than the 101-to 102-mm dividing point selected in 1982.
Appendix Table 3 prov ides all of the length and weight data collected
along with the slide numbers on which the scales are mounted. This scale
collection is available to ADF&G from FRI if required in future studies.
4.1.5 Length-Freauency Evaluation
All length-frequency information collected for fry and smolt is tabu-
lated (Appendix Table 2). No effort to manipulate these data was attempted
in 1983. As in 1982 (Dames & Moore 1982), most of the data are for smolt and
not for fry.
30
~r-----------------------------------------------------------------------------------" o
0'
Z o • -I'.) o
I'.)
(,) ,
o -(,) ,
I'.) o
"'11
~.
c ..
tJ)
-~---
--'
i
i
I
97,~
/
100.,19
/
'-'~9',i9
LEGEND:
, ;:::::.:.
-.::::, .~,
'. '>':'\'
,I
1
101,2
\
\
97,21 z Length in mm, scale slide number
96,3
/
163{14
I • ~
;"' I, '\' \ \ "\ ~
\ "<.
Selected Scales (x 34) of Newhalen River
Sockeye Smolt, RM 13, 1983
~ .. ________________________ ................ ________ ................................................ .J
C-o
D'
Z
0 • ....
I\)
0
I\)
(,)
I
0 ....
(,)
I
I\)
0
w
N
"TI cO·
e: .,
CD
20
15
+J
0
E
(/)
4-10 0
s....
Q)
..0
E
:::I z
5
co co · · +J +J · iio co co · · · U U · · · · · ·
75 80 85 90 95 100
Smolt length in mm
LEGEND:
-1+
...... 2+
n = 184
-· · · · · • · · · · · · · · · · · · · · · · · · · · · · · • · · · · · · · · · · · · · · · · • · · · · · · · · · · · · · · · iii • · · · · · · · · · · · · · · · · · · · · · · · · · · · · · · · · · · · · · · · · · · · · · · · · · · · · · · · · · · -• · · · · · · · · · · · · · · · · · · • · · · • · • • · · · · · • • · • •
105 110 115 120
Sockeye Smolt Age -Length Relationships,
RM 13, Newhalen River, 198~
~ ...................................................................................... ----------------............ ..
Fry: As in 1982, the small numbers of fry measured indicated no real
growth pattern over the period May 16 to June 22 when they were measured. Of
interest and related to fry length was the fact that "unbuttoned" fry were
seen both in early and late spring sampling, possibly indicating the close
proximity of a fry source(s) to RM 13.
Smolt: Computer time, as well as other analytical time, was not
budgeted in 1983 for length-frequency eval uations. Eval uations were made
in 1982.
The striking contrast between 1982 and 1983 is the change in dominance
of age classes. In 1982, 1+ smolt from the large 1980 adult escapement of
1.5 million dominated all smolt catches. In 1983, the same adult escapement
produced a group of 2+ smolt that dominated the spring period outmigration of
smolt •
4.1.6 Other Fish Observations
As indicated in the catch tables by gear type (Appendix Table 1), few
other fish species were taken at RM 13, much as at RM 7 in 1982. Cottids
again dominated the other fish taken. Small Arctic char also were present
along with incidental catches of sucker, cisco, sticklebacks, whitefish, and
one burbot.
Visual and hook-and-line efforts indicated larger resident fish were
present at RM 13 as sampling began. In 1982, few resident fish were seen
until early June (Dames & Moore 1982). A sizeable popUlation of Arctic
char and grayling developed behind ho Iding pens and our fish count-and-
release area. A few rainbow trout were also located there. A single
lake trout was also captured there by hook-and-line.
4.1.7 Final Comments
The cabled net' sampling system used in 1983 at Rt~ 13 had one major
drawback which was fish mortality. When the nets were new and velocities
33
were lower in the earl y spr ing season, few mortal it ies were noted if set
times were held to 15 or 30 minutes when large numbers of fry or smolt
were expected. Later in the season as the cod end of the 9x9-foot nets
sagged and as water velocities increased, more mortalities of juvenile
fish, especially fry, were noted. Mortalities were corrected as far as
possible with reduced net fishing times. We did not feel that sampling
for less than 15 minutes was practical considering that some fishing time
occurs both when the net is being set and retrieved.
The IPT on the other hand had few mortalities except when a "catching
bag" was placed in the IPT live box. This netting restricted fry movement
and in higher velocity periods combined to cause some mortalities. The net
was no longer used once this situation was recognized as a problem.
Any future work should look to reducing fry and smolt mortality either
through reduced handling--more acoustic attempts and/or other gear types such
as larger IPTs fishing deeper which divert fish to a live car rather than
funnel them down a net into a hose and into a live car.
4.2 SUMMER STUDIES
As RM 13 was demobilized in late June 1983, the RM 22 adult counting
camp was mobilized. FRI completed all juvenile and adult sampling at this
site, which operated from June 28 to August 13, 1983.
4.2.1 Juvenile Observations
The IPT, moved up to RM 22 from RM 13, only caught ten sockeye fry and
two sculpins. The reasons for the low 1983 catches are not clear. The IPT
I'las placed in a deeper channel area nearer to the east bank of the river.
With the poor success of the IPT at smolt capture in 1983 at RM 13, it is not
surprising that no smolt or yearlings were taken. ~!hile fry continued to
move past RM 22 in small numbers in the summer and fall 0 f 1982, either no
fry moved in the summer of 1983 or the IPT did not capture them. No conc-
lusions can be drawn except that few fish were taken in 1983.
34
4.2.2 Adult Observations
Table I presents the daily adult sockeye escapement evaluation for RM 22 in 1983.
The total estimated escapement in 1983 was 702,792 adult sockeye salmon. Some
Iqiuqig-taqged adults were also observed at RM 22. The results of this taqgino study
will be available from the University of Alaska, Juneau, after the sturly ends and
analyses are completed.
4.3 FISH DIVERSION AND IMPINGEMENT SURVIVAL STUDIES
Results of diversion tests with smolt 000-120 mm) clearly inrlicaterl that these fish
are capable of easily swimming against the velocities tested. Upon release into the
flow, the smolt distributed across the flume; some diverted within several minutes to
the bypass while others remained in the flume for up to several hours.
Diversion tests with fry (28-32 mm) indicate that this life stage rioes not respond
strongl y to an angled screen. At a velocity of 1.0 foot per second, most of the fry
impinged on the screen upon release but qradually worked their way to the bypass.
Impingement was relatively random in terms of fry orientation (i.e., head first, tail
first, up-side down, etc.) indicating that the fish were qenerally overcome by the
current without being able to orient into it.
Similar results were noted with fry at 0.9, 0.7, 0.6 and 0.5 feet per second velocities.
However, as the velocity decreased, more fish were able to divert to the bypass
without impingement. Nonetheless, even at 0.5 feet per seconrl, some impingement
was noted.
Results of fry impingement tests are summarized in Table 2. Mean survival at the
mesh size/impingement duration combinations tested ranged from 87.3 percent to 95.8
percent. Contingency table analyses indicated no significant differences in survival
between the four test conditions. Therefore, the data can be combined to yield an
overall mean survival value of 93.1 percent. Since the mean control survival was 93.4
percent, the differential mortality between test and control fish was essentially zero.
Therefore, under the conditions tested, it can be expected that sockeye salmon
survival would approach 100 percent in a screening system involving impingement and
removal to a return location in the river.
35
TABLE 1
NEWHALEN RIVER (RM 22) ADULT SOCKEYE ESCAPEMEN T , 1983
Date Daily Cumulative Date Daily Cumulative
June 28 0 0 July 21 17,274 452,454
29 6 6 22 9,870 462,324
30 0 6 23 11,874 474,198
July 0 6 24 10,920 485,118
2 18 24 25 8,232 493,350
3 9,858 9,882 26 15,090 508,440
4 18,210 28,092 27 14,400 522,840
5 34,854 62,946 28 18,840 541,680
6 40,014 102,960 29 23,826 565,506
7 41,376 144,336 30 25,518 591,024
8 29,844 174,180 31 19,188 610,212
9 18,624 192,804 August 1 14,334 624,546
10 14,670 207,474 2 13,422 637,968
11 16,104 223,578 3 15,504 653,472
12 30,246 253,824 4 13,692 667,164
13 26,472 280,296 5 13,212 680,376
14 44,850 325,146 6 6,432 686,808
15 27,852 352,998 7 9,378 696,186
16 19,836 372,834 8 684 696,870
17 23,724 396,558 9 1,176 698,046
18 10,320 406,878 10 1,452 699,498
19 10,608 417,486 11 1,206 700,704
20 17,694 435,180 12 1,392 702,096
13 696 702,792
36
TABLE: 2
SUMMARY OF FRY IMPIt'-lGEMENT DURATION TEST RESUL TS
A) Mean Survival at Each Test Condition
Impingement Duration
Mesh Size
I.O-mm
2.0-mm
8-Min.
.9444
(n=6)
.9583
(n=5)
B) Mean Overall Test Survival = .9313
C) Mean Survival for Each Duration and Mesh Si ze
Duration:
Mesh Size:
8-min. = .9558
16-min. = .9071
I-mm = .9064
2-mm = .9627
D) Mean Control Survival = .9342
E) Mean Differential Mortality
16-Min •
. 8725
(n=5)
.9505
(n=4)
Differential Mortality = Test Mortality -Control Mortality
= (l -.9313) -(l -.9342)
= .0687 -.0658
= .0029 or 0
37
5.0 CONCLUSIONS
5.1 SPRING STUDIES
1. A 7-\<Ieek field effort in 1983 involving net and trap sampling of
juvenile sockeye salmon was completed at RM 13 on the Newhalen
River, Alaska as part of an ongoing hydropower feasibility study.
2. Sampling was completed on a very dynamic river system with changing
climatic and light conditions.
3. In the period from May 11 to June 22, some 1,150 observations of
sockeye smolt and fry catches from nets and an inclined plane
trap (IPT) enumerated over 23,000 smolt and over 100,000 fry.
Some smolt and fry catches were subsampled for length, weight,
and scales.
4. While fry and smolt favored the mid-river area at RM 13, there
was not the distinct "fast lane" observed in 1982 at RM 7. The
reasons for this are not clear but different site conditions are
likely a major factor.
5. Vertical patterns of fry in 1983 appeared similar to 1982. Fry
favor the water column near the surface. Smolt, on the other
hand, appeared to run deeper at RM 13 (1983) than at m~ 7 (1982).
Possible causes include different site conditions and the dominance
of 2+ smolt in 1983. In 1982, 1+ smolt dominated. Other factors
may be involved including closer proximity at RM 13 to smolt sources
(Six-Mile Lake and Lake Clark) than existed at RM 7.
6. The temporal distribution of smolt in 1983 appeared to peak in a
very sporad ic way about May 23 to 26 or about the same time as
in 1982. The temporal distribution of smolt in 1983 indicates
the large nets began operation near the middle of the overall
38
smolt outmigrat ion. However, other smaller nets did not catch
large numbers of smolt between May 16 and 21. Smolt were present as
sampling started and ended.
7. The temporal distribution of fry in 1983 appeared similar to that
of fry in 1982. Fry peaked about June 7 to 10 in 1982. The peak
was about June 9 to 15 in 1983. As in 1982, the 1983 fry appeared
cued to increasing river flows. Fry were present as sampling
started and ended.
8. The estimated number of smolt passing RM 13 from May 20 to June 19
in 1983 was 330,000. A confidence interval was not calculated but
may approach 50 percent due to the inconsistent relationships seen
between the index station and other stations at RM 13. The esti-
mated number of fry passing RM 13 from May 16 to June 21 in 1982 was
1.3 million. A confidence interval was not calculated. The better
data set in 1983 should place the interval below 50 percent.
9. Some 184 of the 209 smolt scales taken in 1983 were aged and,
with the exception of one scale, a length separation point of 97
to 98 mm could be selected between 1+ and 2+ smolt.
10. Length-frequency data for fry in 1983 indicate little growth
through the spring season as seen in 1982. Smol t data indicate
that 2+ smolt almost completely dominated catches in 1983. In
1982, 1+ smolt were more numerous than 2+ smolL The large 1980
adult escapement to the Newhalen River system explains this change
in smolt age in 1982 and 1983.
11. Cottids, as in 1982, dominated the catch of other fish species
i n 1 9 8 3 a t R t~ 1 3 • Arc tic c h a r, s u c k e r, cis co, r a i n bow t r 0 u t ,
stickleback, and whitefish were also taken. One burbot and one
lake trout were also captured at RM 13.
39
12. The large cahled nets, while more efficient on fry anrl smolt, unfortunately
caused mortality problems for the fish, especially as the spring season
proqressed. Sampling times were shortened to reduce this problem.
5.2 SUMMER STUDIES
I. Few juvenile sockeye salmon were taken in an IPT at RM 22 in the period June
28 to August 13, 1983. No explanation exists for this observation.
2. Adult sockeye counts from June 28 to August 13 totaled 702,792 fish, well ahove
1981 and 1982, and helow the 1980 escapements to the Newhalen River system.
5.3 FISH DIVERSION AND IMPlr---IGEMENT SURVIVAL STUGIES
I. Sockeye salmon smolts appear to have the capabi lity for complete diversion in an
angled screen system at low velocities ( 1.1 feet per second).
2. Further studies are needed to quantify smolt diversion and survival at velocities
higher than 1.3 feet per second.
3. Sockeye fry are not capable of divert inq along an anglerl screen, even at low
velocities; therefore, in order to protect the fry, a collection system would be
required.
4. Sockeye fry are capable of wi thstanding impingement on a fine mesh screen (1.0-
and 2.0-mm) wi th very high survival at relat ively low velocities (1.0 fps or less).
5. Hi gher approach velocities in the power canal would reduce costs; smolt appear
to have the potential for diverting at high velocity; similarly, it would appear
that fry could survive impinqement at substantially higher velocities; therefore,
further investigations of the angled screen diversion/collection system should
concentrate on diversion and impingement survival at hiqher velocities than
those usen for this study.
40
6. Because of the favorable results obtaim~rl from the 1983 fish diversion and
impingement studies, the next logical step in determining the feasibility of the
Newhalen River Hydroelectri c Pro ject would be to concluct 8 fish divArsion
demonstration program on the Newhalen River. This program woulcl employ
facilities constructed at the edge of the river that would permit qU8ntitive
experiments over a longer period of time, concentrating on those parameters
that appear to be most critical for fish protection. Such a program would
produce necessary data for engineering design of the intake canal. The program
woulcl also provide a visual demonstration to Bristol Bay residents and interested
fisheries agencies regarding the effectiveness of a diversion system for
protection of downstream juvenile sockeye salmon migrants.
41
6.0 REFERENCES
Dames & Moore, 1982. Bri stol Bay Regional Power PI an, Newhalen River
Juvenile Sockeye Salmon Studies. Prepared for Alaska Power Authority through
Stone & Webster Engineering r:orporation.
Poe, P.H. ami O.A. Mathisen, 1982. 1981 Newhalen River Sockeye Escapement
Studies. University of Washington, Fisheries Research Institute. Report Alaska
Department of Fish & Game. Contract 81-827. Report No. FRI-UW-8211.
Poe, P.H., O.A. Mathisen, and W.R. Lew, 198). 1982 i'lewhalen River Sockeye
Escapement Studies. University of Washington, Fisheries Research Institute.
Report to Alaska Department of Fish and Game. Contract No. 82-1257. Report
No. FRI-UW-8308.
Stone & Webster Engineering Corporation, 1982. Bristol Bay Reqional Power
Plan Detailed Feasibility Analysis, Interim Feasibility Assessment. Prepared for
Alaska Power Authority.
42
A
P
;p
E
N
'0
;J
c
E
S
APPENDIX 1
NEWHALEN RIVER (RM 13) CATCHES 1983
• Inclined Plane Trap
• 9x9-Foot Upstream Net
• 9x9-Foot Downstream Net
• 9x9-Foot Net
• 4x4-Foot East Net
• 3x3-Foot west Net
• 3x9-Foot Net
NEWHALEN RIVER (RM-13) CATCHES, 1983
IPT Sheet 1 of 12
Si te Time Hours Sockeye Sockeye Stickle-Arctic Least Gray-Lake Rainbow White-
Date Code Set Fished Fry Smolt backs Char Cisco ling Cottid Trout Trout fish
5-16-83 2130 1.0 0 0
2300 1 .0 5
5-17-83 0000 1 .0 3 1
0100 1 .0 4 0
0200 1.0 2 0
0300 1.0 3 0
0400 1.0 1 0
1200 8.0 0 0
2200 1 .0 5 0
2300 1.0 16 0
5-18-83 0000 1 .0 9 1
0100 1.0 19 4
0200 1 .0 8 1
0300 1.0 3 0
0400 8.0 0 0
1200 10.0 0 0
2200 1.0 0
2300 1.0 17 0
5-19-83 0000 1 .0 20 0
0100 1.0 18 1
0200 1 .0 15 0
0300 1 .0 2 0
0400 8.0 0 0
1200 4.0 0 0
NEWHALEN RIVER (RM-13) CATCHES, 1983
IPT Sheet 2 of 12
Site Time Hours Sockeye Sockeye Stickle-Arctic Least Gray-Lake Rainbow White-
Date Code Set Fished Fry Smolt backs Char Cisco ling Cottid Trout Trout fish
5-19-83 1600 6.0 0 0
2200 1.0 1 0
2300 1.0 15 1
5-20-83 0000 1 .0 21 0
0100 1.0 12
0200 1 .0 22 1
0300 1 .0 15 0
0400 8.0 6 0
1200 2.5 1 0
1430 6.5 0 0
2100 1.0 1 0
2200 1 .0 3 0
2300 1.0 24 4
5-21-83 0000 1.0 37 0
0100 1.0 16 0
0200 1.0 26 0
0300 1 .0 7 0
0400 1.0 0 0
1200 8.0 0 0
2100 9.0 1 0
2200 1.0 3 0
2300 1.0 26 0
5-22-83 0000 1 .0 25 2
0100 1.0 22
NEWHALEN RIVER ( RM-13) CATCHES, 1983
1FT Sheet 3 of 12
Site Time Hours Sockeye Sockeye Stickle-Arctic Least Gray-Lake Rainbow White-
Date Code Set Fished Fry Smolt backs Char Cisco ling Cottid Trout Trout fish
5-22-83 0200 1.0 15 1
0300 1.0 4 0
0400 8.5 0 0
1230 0 0
2200 1.0 0 0
2300 1.0 26 0
5-23-83 0000 1.0 31 2
0100 1.0 22 0
0200 1.0 12 0
0300 1.0 20 0
0400 8.0 0 0
1200 6.0 0 0
1800 3.0 0 0
2100 1.0 0 0
2200 1.0 1 0
2300 1.0 29 0
5-24-83 0000 2.0 47 0
0200 1.0 42 0 1
0300 1.0 1 0
0400 1.0 1 0
1200 8.0 0 0
1400 6.0 0 0
2200 4.0 69 1
0030 2.5 110 0
NEWHALEN RIVER (RM-13 ) CATCHES, 1983
IPT Sheet 4 of 12
Site Time Hours Sockeye Sockeye Stickle-Arctic Least Gray-Lake Rainbow White-
Date Code Set Fished Fry Smolt backs Char Cisco ling Cottid Trout Trout fish
5-25-83 0400 8.0 0 0
1200 8.0 0 0
2100 4.0 0 0
5-26-83 0000 1.0 70 4
0100 1.0 108 0
0200 1.0 85 0
0300 1.0 14 0
0400 9.0 0 0
1300 8.0 4 0
2100 3.0 134 0
5-27-83 0100 2.0 86 0
0300 1.0 0 0
0400 8.0 0 0
1200 5.0 0 0
1700 4.0 0 0
2100 1.0 0 0
2200 1.0 1 0
2300 1.0 31 0
5-28-83 0000 1.0 115 0
0100 1.0 75 0
0200 1.0 62 0
0300 1.0 11 0
0400 9.0 0 0
1300 8.0 0 0
NEWHALEN RIVER ( RM-13) CATCHES, 1983
IPT Sheet 5 of 12
Site Time Hours Sockeye Sockeye Stickle-Arctic Least Gray-Lake Rainbow White-
Date Code Set Fished Fry Smolt backs Char Cisco ling Cottid Trout Trout fish
5-28-83 2100 1.0 0 0
2200 1.0 1 0
2300 1.0 45 0
5-29-83 0000 1.0 82 0
0100 1.0 74 0
0200 1.0 28 0
0300 1.0 22 0
0400 8.5 9 0
1230 8.5 0 0
2100 1.0 9 0
2200 1.0 9 0
2300 1.0 45 0
5-30-83 0000 1.0 55 1
0100 1.0 59 0
0200 1.0 24 0
0300 1.0 6 0
0400 8.0 0 0
1200 9.0 0 0
2100 1.0 0 0
2200 1.0 0 0
2300 1.0 9 0
5-31-83 0000 1.0 62 0
0100 1.0 32 0
0200 1.0 71 0
NE:WHALEN RIVER (RM-13) CATCHES, 1983
IPT Sheet 6 of 12
Si te Time Hours Sockeye Sockeye Stickle-Arctic Least Gray-Lake Rainbow White-
Date Code Set Fished Fry Smolt backs Char Cisco ling Cottid Trout Trout fish
5-31-83 0300 1.0 16 1
0400 4.0 0 0
1200 9.0 0 0
2100 1 .0 0 0
2200 1 .0 4 0
2300 1.0 41 0
6-01-83 0000 1 .0 15 0
0100 1 .0 61 0
0200 1.0 13 0
0300 1 .0 10 0
0400 8.0 6 0
1200 9.0 0 0
2100 1.0 0 0
2300 2.0 32
6-02-83 0000 1.0 80 0
0100 1.0 78 0
0200 1.0 23 0
0300 1.0 3 2
0400 8.0 O(a) O(a)
1200 9.0 O(a) O(a)
2200 1 .0 61 0
2300 1.0 23 0
0000 1.0 95 0
(a) IPT flooded, some fish likely lost.
NEW HAL EN RIVER (RM-13) CATCHES, 1983
IPT Sheet 7 of 12
si te Time Hours sockeye Sockeye Stickle-Arctic Least Gray-Lake White-
Date Code Set Fished Fry Smolt backs Char Cisco ling Cot tid Trout Sucker fish
6-03-83 0100 1.0 55 0
0200 1 .0 68 0
0300 1 .0 21 0
2000 1.0 0 0
2100 1.0 0 0
2200 1.0 4 0
2300 1.0 71 0
6-04-83 0000 1.0 67 0
0100 1.0 45 0
0200 1.0 30 0
0300 1 .0 5 0
2100 1 .0 2 0
2200 1.0 1 0
2300 1.0 34 0
6-05-83 0000 1 .0 83 4
0100 1.0 74 0
0200 1 .0 23 0
0300 1.0 10 0
2100 2.0 1 0
2300 1 .0 34 0
6-06-83 0000 1 .0 117 0
0100 1.0 99 0
0200 2.0 15 0
NEWHALEN RIVER (RM-13) CATCHES, 1983
IPT Sheet 8 of 12
Site Time Hours Sockeye Sockeye Stickle-Arctic Least Gray-Lake Rainbow White-
Date Code Set Fished Fry Smolt backs Char Cisco ling Cot tid Trout Trout fish
6-07-83 0000 1 .0 238 0
0100 1 .0 248 0
0200 1 .0 162 1
0300 1 .0 11 0
2100 1 .0 4 0
2200 1 .0 10 0
2300 1.0 230 0
6-08-83 0000 1 .0 323 0
0100 1 .0 273 0
0200 1.0 200(b) 0
0300 1 .0 96 0
2100 1 .0 2 0
2200 1 .0 14 0
2300 1.0 202 0
6-09-83 0000 1 .0 607 0
0100 1.0 550 0
0200 1.0 300 0
0300 1.0 28 0
2100 1.0 17 0
2200 1 .0 61 0
2300 1.0 577 0
6-10-83 0000 1 .0 929 0
0100 1 .0 892 0
0200 1 .0 563 0
(b) Estimate of catch as counter broke and di,_l not record all fish.
NEWHALEN RIVER (RM-13) CATCHES, 1983
IPT Sheet 9 of 12
Site Time Hours Sockeye Sockeye Stickle-Arctic Least Gray-Lake White-
Date Code Set Fished Fry Smolt backs Char Cisco ling Cot tid Trout Sucker fish
6-10-83 0300 1.0 11 0
2100 1 .0 2 0
2200 1 .0 15 0
2300 1.0 436 0
6-11-83 0000 1.0 1,096 0
0100 1 .0 1,078 0
0200 1 .0 673 0
0300 1 .0 132 0
2100 1 .0 7 0
2200 1 .0 35 0
2300 1 .0 300 0
6-12-83 0000 1 .0 638 0
0100 1.0 824 0
0200 1.0 1,252 (j
0300 1 .0 156 0
2100 1.0 3 0
2200 1 .0 7 0
2300 1 .0 196 0
6-13-83 0000 1.0 531 0
0100 1.0 790 0
0200 1.0 1 ,581 0
0300 1 .0 162 0
2100 3.0 83 0
6-14-83 0000 1.0 433 0
NEWHALEN RIVER (RM-13 ) CATCHES, 1983
1FT Sheet 10 of 12
Site Time Hours Sockeye Sockeye Stickle-Arctic Least Gray-Lake White-
Date Code Set Fished Fry Smolt backs Char Cisco ling Cottid Trout Sucker fish
6-14-83 0100 1.0 426 0
0200 1.0 548 0
0300 1.0 43 0
2100 1.0 0 0
2200 1.0 4 0
2300 1.0 77 0
6-15-83 0000 1.0 318 0
0100 1.0 521 0
0200 1.0 1,700 0
0300 1.0 212 0
2100 1.0 6 0
2200 1.0 22 0
2300 1.0 46 0
6-16-83 0000 1.0 303 C
0100 1.0 468 0
0200 1.0 718 0
0300 1.0 217 0
2100 1.0 0 0
2200 1.0 0 0
2300 1.0 54 0
6-17-83 0000 1.0 280 0
0100 1.0 467 0
0200 1.0 458 0
0300 1.0 28 0
NEWHALEN RIVER (RM-13) CATCHES, 1983
1FT Sheet 11 of 12
Site Time Hours Sockeye Sockeye Stickle-Arctic Least Gray-Lake White-
Date Code Set Fished Fry Smolt backs Char Cisco ling Cottid Trout Sucker fish
0400 9.0 0 0
1300 8.0 0 0
2100 1.0 0 \J
2200 1.0 1 0
2300 1.0 93 0
6-18-83 0000 2.0 456 0
0200 1.0 305 0
0300 1.0 8 0
2100 1.0 9 0
2200 1.0 9 0
2300 1.0 65 0
6-19-83 0000 1.0 308 0
0100 1.0 386 0
0200 1.0 492 0
0300 1.0 40 0
0400 1.0 0 0
1300 7.5 0 0
2130 1.5 0 0
2300 1.0 7 0
6-20-83 0000 1.0 78 0
0100 1.0 331 0
0200 1.0 160 0
2100 1.0 0 0
2200 1.0 0 0
Site
Date Code
6-20-83
6-21-83
6-22-83
Time
Set
2300
0000
0100
0200
0300
2100
2200
2300
0000
0100
0200
0300
,~'t!-,
'J
Hours
Fished
1.0
1 0
1.0
1.0
1.0
1.0
1.0
1.0
1.0
1.0
1.0
1.0
NEWHALEN RIVER (RM-13) CATCHES, 1983
IPT
Sockeye Sockeye Stickle-Arctic Least
Fry Smolt backs Char Cisco
20 0
70 0
134 0
126 0
3 0
0 0
0 0
5 0
52 0
138 0
85 0
1 0
Sheet 12 of 12
Gray-Lake White-
ling Cottid Trout Sucker fish
NEWHALEN R rVER (RM-l 3 ) CATCHES, 1983
9 X 9-FOOT UPSTREAM Sheet 1 of 6
Site Time Hours Sockeye Sockeye Stickle-Arctic Least Gray-Lake
Date Code Set Fished Fry Smolt backs Char Cisco ling Cottid Trout Sucker Burbot
5-26-83 3 2100 0.5 0 0
3 2200 0.5 5 8
3 2300 0.5 90 66
5-27-83 3 0000 0.5 72 0 6
3 0100 0.5 62 37 2
3 0200 0.5 3 16
3 0300 0.5 0 0
3 0400 gear failure
3 1200 2.0 4 91
3 1400 3.0 0 3
3 1700 3.5 0 0
5 2030 0.5 0
5 2130 0.5 0 0
5 2230 0.5 0 4
5 2330 0.5 111 0
5-28-83 5 0030 0.5 430 13 4
5 0130 0.5 298 4
5 0230 0.5 69 8
5 0330 0.5 1
5 0430 8.0 0 0
2 2100 1.0 0 0
2 2200 1 .0 0 0
2 2300 1 .0 16
5-29-83 2 0000 1.0 79 2
NEWHALEN RIVER (RM-13) CATCHES, 1983
9 X 9-FOOT UPSTREAM Sheet 2 of 6
Site Time Hours Sockeye Sockeye Stickle-Arctic Least Gray-Lake
Date Code Set Fished Fry Smolt backs Char Cisco ling Cottid Trout Sucker Burbot
5-29-83 2 0100 1.0 67 0
2 0200 1.0 11 2
2 0300 1 .0 0 0
2 0430 8.0 0
3 2100 1.0 25
3 2200 1 .0 0
3 2300 1.0 39 172 2
5-30-83 3 0000 1.0 103 27 6
3 0100 1 .0 118 0 3
3 0200 1.0 43 0
3 0300 1.0 5
3 0400 8.0 0
5 2100 1.0 0 0
5 2200 1 .0 1 0
5 2300 1 .0 95 43
5-31-83 5 0000 1 .0 498 5 5
5 0100 1.0 289 78
5 0200 1 .0 278 66
5 0300 1 .0 18 2
5 0400 1.0 0 11
5 0500 7.0 0 0
2 2100 1 .0 0 0
2 2200 1 .0 0 0
2 2300 1.0 29 0
NEWHALEN RIVER (RM-13) CATCHES, 1983
9 X 9-FOOT UPSTREAM Sheet 3 of 6
Site Time Hours Sockeye Sockeye Stickle-Arctic Least Gray-Lake
Date Code Set Fished Fry Smolt backs Char Cisco ling Cottid Trout Sucker Burbot
6-01-83 2 0000 1.0 538 0 3
2 0100 1 .0 23 0 7
2 0200 1.0 17 0 2
2 0300 1.0 0
2 0400 8.5 0 1
3 2100 1.0 0
3 2200 1 .0 0 1,384
3 2300 1.0 18 606
6-02-83 3 0000 1.0 45 430 2
3 0100 1.0 97 724 2
3 0200 1.0 25 386
3 0300 1.0 8 636
3 0400 1.0 2
3 0500 8.0 0 12
5 2300 1.0 262 7
6-03-83 5 0000 1 .0 636 66
5 01 00 0.5 464 15
5 0200 0.5 232 7
5 0300 0.5 62 2
5 0400 0.5 2 2
5 0430 gear not fished
5 2030 0.5 0 0
5 2130 0.5 0 0
5 2230 0.5 0
I I I I I I I I I I I I I I
NEWHALEN RIVER (RM-13) CATCHES, 1983
9 X 9-FOOT UPSTREAM Sheet 4 of 6
Site Time Hours Sockeye Sockeye Stickle-Arctic Least Gray-Lake
Date Code Set Fished Fry Smolt backs Char Cisco ling Cottid Trout Sucker Burbot
6-03-83 2 2330 0.5 18 2
6-04-83 2 0030 0.5 31 0
2 0130 0.5 12 0 2 1
2 0230 0.5 18 0
2 0330 1.0 4 0
3 2100 1.0 0 369
3 2200 1.0 0 91
3 2300 1.0 48 142
6-05-93 3 0000 1.0 17 184 1
3 0100 1.0 205 60
3 0200 1.0 89 41
3 0300 1.0 10 47
3 2100 gear failure
6-06-83 5 0000 1.0 650 14 1 1
5 0100 1.0 1,481 5
5 0200 0.5 392 7
5 0300 0.5 76 35
5 0400 0.5 3 0
2 2315 0.5 27 0
6-07-83 2 0000 1.0 149 96
2 0100 1.0 361 3 1 1
2 0200 1.0 43 4 2 1
1 0300 1.0 7 0
4 2100 1.0 2 0
NEWHALEN RIVER (RM-13) CATCHES, 1983
9 X 9-FOOT UPSTREAM Sheet 6 of 6
Site Time Hours Sockeye Sockeye Stickle-Arctic Least Gray-Lake
Date Code Set Fished Fry Smolt backs Char Cisco ling Cottid Trout Sucker Burbot
6-11-83 4 0230 0.25 684 2
4 0300 1.0 107
5 2100 1.0 0 0
5 2200 1.0 26 0
5 2300 1.0 807 2
6-12-83 5 0030 0.25 1,085 0 2
5 0130 0.25 464 0
5 0230 0.25 398 0
5 0300 1.0 22 0
2 2100 1.0 0 0
2 2200 1.0 0 0
2 2300 1.0 9 0
6-13-83 2 0020 0.5 71 4
2 0120 0.5 51 0
2 0220 0.5 46 0
2 0320 0.5 5 0
2 0420 gear failure
NEWHALEN RIVER (RM-13) CATCHES, 1983
9 X 9-FOOT DOWNSTREAM Sheet 1 of 9
Site Time Hours Sockeye Sockeye Stickle-Arctic Least Gray-Lake White-
Date Code Set Fished Fry Smolt backs Char Cisco ling Cot tid Trout Sucker fish
5-24-83 4 2100 1.0 0 712
4 2230 0.5 0 4,000(a)
4 2330 0.5 48 388 2
5-25-83 4 0030 0.5 286 471 2
4 0130 0.5 54 978
4 0245 0.5 22 228
4 0330 0.5 4 50
4 0430 7.5 0 8
4 1200 9.0 0 0
4 2100 0.5 630
4 2200 0.5 0 796
4 2300 0.5 26 719
5-26-83 4 0000 gear failure
4 1530 4.5 0 1
4 1900 pulled for cleaning
4 2100 0.5 0 2
4 2200 0.5 8 10
4 2300 0.5 303 30
5-27-83 4 0000 0.5 311 8
4 0100 0.5 224 13
4 0200 0.5 12 31
4 0300 0.5 0 0
4 0400 8.0 1 110
4 1230 0.5 0 0
(a) Estimated catch based upon weighed samples.
NEWHALEN RIVER (RM-13) CATCHES, 1983
9 X 9-FOOT DOWNSTREAM Sheet 2 of 9
Site Time Hours Sockeye Sockeye Stickle-Arctic Least Gray-Lake White-
Date Code Set Fished Fry Smolt backs Char Cisco ling Cottid Trout Sucker fish
5-27-83 7 1750 4.5 0 3
4 2030 0.5 1 1
4 2130 0.5 0 0
4 2230 0.5 1
4 2330 0.5 125 13
5-28-83 4 0030 0.5 460 19
4 0130 0.5 288 9 1
4 0230 0.5 69 45
4 0330 0.5 2 3
4 0430 8.0 0 32
4 2100 1.0 0 11
4 2200 1.0 0 0
4 2300 1.0 76 3 1
5-29-83 4 0000 1.0 400 28 2
4 0100 1.0 459 2 6
4 0200 1.0 81 11 1
4 0300 1.0 6 18
4 0430 8.0 0 2
4 2100 1.0 0 0
4 2200 1.0 9 0
4 2300 1.0 301 143
5-30-83 4 0000 1.0 967 76 2
4 0100 1.0 600 3
4 0200 1.0 167 0 1
NEWHALEN RIVER (RM-13) CATCHES, 1983
9 X 9-FOOT DOWNSTREAM Sheet 3 of 9
Site Time Hours Sockeye Sockeye Stickle-Arctic Least Gray-Lake White-
Date Code Set Fished Fry Smolt backs Char Cisco ling Cottid Trout Sucker fish
5-30-83 4 0300 1.0 11 0
4 0400 8.0 0 3
4 2100 1.0 1 0
4 2200 1.0 2 0
4 2300 1.0 35 111
5-31-83 4 0000 1.0 429 222
4 0100 1.0 403 152 2
4 0200 1.0 175 141 1
4 0300 1.0 11 154
4 0400 8.0 0 3
4 2100 1.0 1 0
4 2200 1.0 0 1
4 2300 1.0 173 2
6-01-83 4 0000 1.0 536 9
4 0100 1.0 595 7 1
4 0200 1.0 130 1 1
4 0300 1.0 14 10
4 0400 8.5 114 0
4 2100 1.0 0 0
4 2200 1.0 0 1,390
4 2300 1.0 87 557
6-02-83 4 0000 1.0 371 340 2
4 0100 1.0 368 468
4 0200 1.0 128 1,098
NEWHALEN RIVER (RM-13) CATCHES, 1983
9 X 9-FOOT DOWNSTREAM Sheet 4 of 9
Site Time Hours Sockeye Sockeye Stickle-Arctic Least Gray-Lake White-
Date Code Set Fished Fry Smolt backs Char Cisco ling Cottid Trout Sucker fish
6-02-83 4 0300 1.0 21 106
4 0400 1 .0 13 100
4 0500 7.0 6 231(a)
4 2200 1.0 14 15
4 2300 1.0 341 94
6-03-83 4 0000 1.0 723 101 3
4 0100 0.5 372 27
4 0200 0.5 194 24
4 0300 0.5 54 8
4 0400 0.5 4 4
4 0430 gear not fished
4 2030 0.5 0 0
4 2130 0.5 1 0
4 2230 0.5 18 1
4 2330 0.5 275 14
6-04-83 4 0030 0.5 289 15
4 0130 0.5 254 25
4 0230 0.5 94 3
4 0330 1.0 14 24
4 2100 1.0 1 117
4 2200 1.0 3 0
4 2300 1.0 108 7
6-05-83 4 0000 1.0 698 31
4 0100 1.0 366 178
(a) Net frame was broken but continued to fish with less frequency
NEWHALEN RIVER (RM-13) CATCHES, 1983
9 X 9-FOOT DOWNSTREAM Sheet 5 of 9
Site Time Hours Sockeye Sockeye Stickle-Arctic Least Gray-Lake White-
Date Code Set Fished Fry Smolt backs Char Cisco ling Cottid Trout Sucker fish
6-05-83 4 0200 1.0 112 80
4 0300 1.0 87 7
4 2100 1.0 gear failure
6-06-83 4(a) 2315 0.5 105 16
6-07-83 4 0000 1.0 969 81
4 0100 1.0 687 102 1
4 0200 1.0 241 53 1
4 0300 0.5 20 1
4 2100 1.0 0 0
4 2200 1.0 11 70
4 2300 1.0 217 62 2 1 1
6-08-83 4 0025 1.0 1,051 1 1
4 0130 0.5 1,075 8
4 0200 0.5 436 13
4 0300 1.0 81 21
4 2100 1.0 4 0
4 2200 1.0 9 38
4 2300 1.0 208 46
6-09-83 4 0000 0.5 640 20
4 0100 0.5 1, 140 105
4 0200 0.25 647 10
4 0300 1.0 100 216
(a) After 0300 on 6-05-83 and the gear failure. the "fixed" downstream net position moved to the west about
30 feet at a position that could be called Station 3.5.
NEWHALEN RIVER (RM-13) CATCHES, 1983
9 X 9-FOOT'DOWNSTREAM Sheet 6 of 9
Site Time Hours Sockeye Sockeye Stickle-Arctic Least Gray-Lake White-
Date Code Set Fished Fry Smolt backs Char Cisco ling Cottid Trout Sucker fish
6-09-83 4 2100 1.0 21 15
4 2200 1.0 22 135
4 2300 1. ° 275 300
6-10-83 4 0015 0.5 1,012 12
4 0130 0.25 669 32
4 0220 0.25 431 3
4 0300 1.0 224 85
4 2100 1.0 6 11
4 2200 1.0 25 0
4 2300 1.0 526 35
6-11-83 4 0000 0.25 713 5
4 0130 0.25 800 3 2
4 0230 0.25 455 0
4 0300 1.0 227 7
4 2100 1.0 3 0
4 2200 1.0 24 2
4 2300 1.0 274 12
6-12-83 4 0030 0.25 562 1 3
4 0130 0.25 558 2
4 0230 0.25 432 3
4 0300 1.0 280 0
4 2100 1.0 0 0
4 2200 1.0 3 11
4 2300 1.0 194 7
NEWHALEN RIVER (RM-13) CATCHES, 1983
9 X 9-FOOT DOWNSTREAM Sheet 7 of 9
Site Time Hours Sockeye Sockeye Stickle-Arctic Least Gray-Lake White-
Date Code Set Fished Fry Smolt backs Char Cisco ling Cottid Trout Sucker fish
6-13-83 3 0030 0.5 737 0
3 0120 0.5 790 1 2
3 0220 0.5 1,146 0 1
3 0320 0.5 37 0
3 2100 1.5 117 1
6-14-83 3 0030 0.5 800 (a) 0
3 0130 0.5 875 0
3 0230 0.5 1, 151 4
3 0300 1.0 245 47
3 0420 0.5 2 0
3 2100 1.0 4 0
3 2200 1.0 6 0
3 2300 1.0 141 26
6-15-83 3 0020 0.5 940 1
3 0130 0.25 480
3 0230 0.25 897 0
3 0300 1.0 69 1
3 2100 1.0 3 0
3 2200 1.0 0 0
3 2300 1.0 114 125
6-16-83 3 0030 0.5 635 7
3 0130 0.25 420 0
3 0230 0.25 563 9
3 0300 1.0 96 9
(a) Approximate count as clicker broke during counting.
NEWHALEN RIVER (RM-13) CATCHES, 1983
9 X 9-FOOT DOWNSTREAM Sheet 8 of 9
Site Time Hours Sockeye Sockeye Stickle-Arctic Least Gray-Lake White-
Date Code Set Fished Fry Smolt backs Char Cisco ling Cottid Trout Sucker fish
6-16-83 3 2100 1.0 1 0
3 2200 1.0 1 0
3 2300 1.0 50 0
6-17-83 3 0000 gear failure
3 2100 1.0 0 0
3 2200 1.0 6 2
3 2300 1.0 185 2
6-18-83 3 0000 0.5 545 11 1 1
3 0130 0.5 717 6
3 0230 0.5 515 7
3 0300 1.0 57 6
3 2100 1.0 1 0
3 2200 1.0 1 0
3 2300 1.0 131 6
6-19-83 3 0000 1.0 775 2~ 2
3 0100 1.0 1,079 20
3 0200 1.0 1,237 10
3 0300 1.0 77 0
3 1630 5.0 0 0
3 2200 1.0 0 0
3 2300 1.0 30 54
6-20-83 3 0000 1.0 379 2 1
3 0100 1.0 442 32 1
3 0200 1.0 362 13
NEWlffiLEN RIVER (RM-13) CATCHES, 1983
9 X 9-FOOT DOWNSTREAM Sheet 9 of 9
Site Time Hours Sockeye Sockeye Stickle-Arctic Least Gray-Lake White-
Date Code Set Fished Fry Smolt backs Char Cisco ling Cottid Trout Sucker fish
6-20-83 3 2100 1.0 0
3 2200 1.0 2 2
3 2300 1.0 34 2
6-21-83 3 0000 1.0 312 2
3 0100 1.0 477 6
3 0200 1.0 442 2
3 0300 1.0 20 59
3 2100 1.0 2
3 2200 1.0 0 0
3 2300 1.0 24 21
6-22-83 3 0000 1.0 272 27
3 0100 1.0 1,034 0
3 0200 1.0 1,079 11
3 0300 1.0 56 0
NEWHALEN RIVER (RM-l 3) CA'l'CHES, 1983
9 X 9-FOOT NET UPSTREAH Sheet 1 of 2
Si te Time Hours Sockeye Sockeye Stickle-Arctic Least Gray-Lake White-
~ate Code Set Fished Fry Smolt backs Char Cisco ling Cot tid Trout Sucker fish
5-20-83 4 1930 1 .5 0 0
4 2100 1.0 2
4 2200 1 .0 2 67
4 2300 1.0 97 125 3
5-21-83 4 0000 1 .0 325 104
4 0100 1.0 335 3 3 3
4 0200 1 .0 198 29
4 0300 1.0 22 71
4 0400 0.5 0
4 0430 7.5 0 49
4 1200 9.0 0 2
3 2100 1 .0 0 0
3 2200 1.0 7 1 1
6 2300 1 .0 4 0 3
5-22-83 5 0000 1.0 144 15 9
2 0100 1.0 18 12
4 0200 1 .0 13 279
1 0300 1.0 6 4
4 0400 8.0 2 49
4 1200 2.5 0 0
4 1430 gear not fished
4 1730 2.5 0 275
4 2200 1 .0 4 0
4 2300 1.0 45 100 3
NEWHALEN RIVER (RM-l 3) CATCHES, 1983
9 X 9-FOOT NE'!' UPSTREAM Sheet 2 of 2
Si te Time Hours Sockeye Sockeye Stickle-Arctic Least Gray-Lake White-
Date Code Set Fished Fry Smolt backs Char Cisco ling Cottid '!'rout Sucker fish
5-23-83 4 0000 1 .0 147 259 3 2
4 0100 1 .0 182 33 7
4 0200 1 .0 102 7
4 0300 1 .0 28 3
4 0400 8.0 0
3.5 2100 1 .0 0 0
3.5 2200 1.0 0 0
3.5 2300 1.0 62 162
5-24-83 3 0000 1 .0 3 1,250 2
3 0100 1.0 14 721 1
3 0200 1 .0 30 570 2
3 0300 1 .0 18 202
3 0400 1.0 0 34
NEWHALEN RIVER (RM-13) CATCHES, 1983
4 x 4-FOOT NET EAST Sheet 1 of 9
Site Time Hours Sockeye Sockeye Stickle-Arctic Least Gray-Lake White-
Date Code Set Fished Fr~ Smolt backs Char Cisco lin2 Cottid Trout Sucker fish
5-11-83 1 (a) 1500 20.0 0 4
5-12-83 1 1100 23.2 0 1
5-13-83 1040 24.2 2 0 2
5-14-83 1 0900 24.0 2 0 1
5-15-83 1 0900 23.2 4 0 1
5-16-83 1 0845 2.7 0 0
1 1100 12.0 0 0
2300 2.5 4 0 2
5-17-83 0130 0.5 4 0 2
1 0200 2.0 2 0
1 0400 8.0 0 0
1200 5.0 0 0
2 1700 5.0 0 0
2 2200 1.0 2 0
2 2300 1.0 2 0
5-18-83 2 OOOO(b) 1.0 6 0
2 0100 1.0 2 0 1
2 0200 1.0 2 0
2 0300 1.0 0 0
2 1)400 8.0 0 0
2 1200 10.0 1 0
2 2200 1.0 1 0
2 2300 1.0 7 0 1
( a) Site 1 and 2 were about 30 feet downstream of upstream cable and about 10 feet and 15 feet, respectively,
from water's edge.
( b) 0000 equals midnight.
NEWHALEN RIVER (RM-13) CATCHES, 1983
4 x 4-FOOT NET EAST Sheet 2 of 9
Site Time Hours Sockeye Sockeye Stickle-Arctic Least Gray-Lake Whi te-
Date Code Set Fished Fry Smolt backs Char Cisco ling Cottid 'l'rout Sucker fish
5-19-83 2 0000 1 .0 6 0 2
2 0100 1.0 8 0
2 0200 1 .0 6 0
2 0300 1.0 0
2 0400 1 .0 0 0
2 1200 1 .0 1 0
2 2200 1.0 3 0
2 2300 1.0 6 0 2
5-20-83 2 0000 1 .0 6 0 2
2 0100 1 .0 7 0 2
2 0200 1.0 4 0
2 0300 1 .0 0 0
2 0400 1 .0 0 0
2 1200 1 .0 0 0
2 1630 2.5 5 0
2 2100 1.0 0 0
2 2200 1.0 2 0
2 2300 1.0 7 0
5-21-83 2 0000 1.0 7 0 2
2 0100 1.0 0 1
2 0200 1 .0 0
2 0300 1 .0 0
2 0400 8.0 2 0
2 1200 9.0 2 0
NEWHALEN RIVER (RM-13) CATCHES, 1983
4 x 4-FOOT NET EAST Sheet 3 of 9
Si te Time Hours Sockeye Sockeye Stickle-Arctic Least Gray-Lake White-
Date Code Set Fished Fry Smolt backs Char Cisco ling Cottid Trout Sucker fish
5-21-83 2 2100 1.0 2 0
2 2200 1 .0 1 0
2 2300 1.0 9 0 3
5-22-83 2 0000 1 .0 2 0 4
2 0100 1 .0 3 0 5
2 0200 1.0 3 0
2 0300 1 .0 0 0
2 0400 8.5 0 0
2 1230 8.5 2 0
2 2200 1.0 0 0
2 2300 1 .0 10 0
5-23-83 2 0000 1 .0 4 0 1
2 0100 1.0 3 0 2
2 0200 1.0 3 0
2 0300 1 .0 0 0
2 0400 8.0 1 0
2 1200 6.0 2 0
2 1800 3.0 0 0
2 2100 1 .0 0 0
2 2200 1.0 0
2 2300 1 .0 8 0 3
5-24-83 2 0000 1 .0 4 0
2 0200 2.0 0 0 2
2 0300 1.0 3
NEWHALEN RIVER (RM-13) CATCHES, 1983
4 x 4-FOOT NET EAST Sheet 4 of 9
Si te Time Hours Sockeye Sockeye stickle-Arctic Least Gray-Lake White-
Date Code Set Fished Fry Smolt backs Char Cisco ling Cot tid Trout Sucker fish
5-24-83 2 0400 8.0 0 0
2 1200 4.0 0 0
2 1600 6.0 0 0
2 2200 2.5 0 0
5-25-83 2 0030 3.5 1 0
2 0400 8.0 0 0
2 2100 3.0 6 0
5-26-83 2 0100 3.0 2 0 3
2 0400 9.0 0 0
2 1300 8.0 0 0
2 2100 1 .0 4 0
2 2200 3.0 10 0 2
5-27-83 2 0100 2.0 2 0
2 0300 1 .0 0 0
2 0400 8.0 0 0
2 1200 5.0 0 0
2 1700 4.0 0 0
2 2100 1 .0 0
2 2300 2.0 12 0
5-28-83 2 0100 2.0 2 0
2 0300 1 .0 2 0
2 0400 8.0 0 0
2 1200 9.0 0 0
NEWHALEN RIVER (RM-l 3) CATCHES, 1983
4 x 4-FOOT NET EAST Sheet 5 of 9
si te Time Hours Sockeye Sockeye Stickle-Arctic Least Gray-Lake white-
Date Code Set Fished Fry Smolt backs Char Cisco ling Cot tid Trout Sucker fish
5-28-83 2100 1.0 0 0
2200 2.0 5 0
5-29-83 0000 1.0 5 0
0100 3.0 3 0
0400 8.5 3 0
1230 8.5 1 0
2100 2.0 0
5-30-83 0000 2.0 11 0
0200 2.0 3 a
0300 1.0 a 0
0400 8.0 0 0
1200 9.0 0 a
2100 3.0 a 0
5-31-83 0000 2.0 14 0
0200 1.0 9 0
0300 1 .0 4 0
0400 8.0 0 0
1200 9.0 0 0
2100 1.0 0 a
2200 2.0 0 0
6-01-83 0000 2.0 2 0
0200 2.0 6 0
0300 1 .0 2 0
0400 8.0 2 0
NEWHALEN RIVER (RM-13) CATCHES, 1983
4 x 4-FOOT NET EAST Sheet 6 of 9
Site Time Hours Sockeye Sockeye Stickle-Arctic Least Gray-Lake White-
Date Code Set Fished Fry Smolt backs Char Cisco ling Cottid Trout Sucker fish
6-01-83 1200 9.0 0
2100 1 .0 0 0
2200 1 .0 0 0
2300 1 .0 a a
6-02-83 0000 1 .0 0 a
0100 1 .0 a 0
0200 1 .0 a a
0300 1 .0 0
0400 21.0 12 a
6-03-83 0100 3.0 2 0
0400 8.0 a a
1200 9.0 1 a
2100 2.0 a a
2200 2.0 18 0
6-04-83 0100 2.0 0
0300 1 .5 a
0430 1 .5 1 a
1200 9.0 a 0
2100 2.0 2 a
2300 2.0 9 a
6-05-83 0100 2.0 2 a
0300 1 .0 1 0
0400 1 .0 0 a
1200 8.0 0 a
NEWHALEN RIVER (RM-13) CATCHES, 1983
4 x 4-FOOT NET EAST Sheet 7 of 9
Site Time Hours Sockeye Sockeye Stickle-Arctic Least Gray-Lake White-
Date Code Set Fished Fry Smolt backs Char Cisco ling Cottid Trout Sucker fish
6-05-83 2100 2.0 2 0
2300 2.0 25 0
6-06-83 0100 3.0 4 0
0400 8.0 0 0
6-07-83 1400 7.0 0 0
2100 2.0 16 0
2300 5.0 0
6-08-83 0400 8.0 0 0
1200 9.0 0 0
2100 3.0 15 0
6-09-83 0000 4.0 21 0
0400 8.0 2 0
1200 3.0 0 0
2100 3.0 38 0
6-10-83 0000 4.0 21 0
0400 8.0 0 0
1200 9.0 7 0
2100 3.0 26 0
6-11-83 0000 4.0 13 0
0400 1.7 8 0
2100 4.0 27 0
6-12-83 0100 3.0 33 0
0400 8.0 0 0
NEWHALEN RIVER (RM-13) CATCHES, 1983
4 x 4-FOOT NET EAST Sheet 8 of 9
Si te Time Hours sockeye Sockeye Stickle-Arctic Least Gray-Lake White-
Date Code Set Fished Fry Smolt backs Char Cisco ling Cottid Trout Sucker fish
6-13-83 1200 9.0 0 0
2100 3.0 5 0
6-14-83 0000 4.0 6 0
0400 8.0 0 0
1200 9.0 0 0
2100 7.0 0 0
6-15-83 0400 17 .0 4 0
2100 7.0 1 0
6-16-83 0400 9.0 0 0
1300 9.0 0 0
2100 7.0 0 0
6-17-83 0400 4.0 0 0
1300 9.0 1 0
2100 8.0 6 0
6-18-83 0000 3.0 15 0
0400 4.0 0 0
1200 8.0 0 0
2100 3.0 6 0
6-19-83 0000 4.0 0
0400 9.0 0 0
1300 9.0 0 0
2200 9.0 0 0
6-20-83 0300 5.0 2 0
1200 9.0 0 0
Si te
Date Code
6-20-83
6-21-83
6-22-83
Time
Set
2130
0100
0400
1730
2100
0000
Hours
Fished
3.5
4.5
13.5
3.5
3.0
4.0
NEWHALEN RIVER (RM-13) CATCHES, 1983
4 x 4-FOOT NET EAST
Sockeye Sockeye Stickle-Arctic Least
Fry Smolt backs Char Cisco
0 0
0 0
0 0
0
1 0
0 0
Sheet 9 of 9
Gray-Lake White-
ling Cottid Trout Sucker fish
NEWHALEN RIVER (RM-13) CATCHES, 1983
3 X 3-FOOT NET WEST Sheet 1 of 10
Site Time Hours Sockeye Sockeye Stickle-Arctic Least Gray-Lake Misc. White-
Date Code Set Fished Fry Smolt backs Char Cisco lin9: Cot tid Trout Salmonid fish
5-13-83 1 (a) 1110 21.5 0 0
5-14-83 1 0846 9.1 1 0 1
1 1730 15.2 1 0
5-15-83 1 0845 5.2 0 0
1 1400 7.5 0 0
1 2230 11.0 2 0
5-16-83 1 0930 2.5 3 0 1
5-17-83 OOOO(b) 1.0 15 0
1 0100 1.0 18 0 2
1 0200 1.0 4 0
1 0300 1.0 0 0
1 0400 1.0 0 0
1 1200 8.0 0 0
1 1730 5.5 0 0
1 2200 1.0 1 0
1 2300 1.0 4 0
5-18-83 1 0000 1.0 7 0
1 0100 1.0 9 0
1 0200 1.0 5 0
1 0300 1.0 5 0
1 0400 8.5 0 0 1
1 1230 9.5 0 0
1 2200 1.0 0 0
1 2300 1.0 4 0 1 1
(a) Site 1 was about 150 feet upstream of the upstream cable and about 40 to 50 feet from water's edge.
( b) 0000 equals midnight.
NEWHALEN RIVER (RM-13) CATCHES, 1983
3 X 3-FOOT NET WEST Sheet 2 of 10
Si te Time Hours Sockeye Sockeye Stickle-Arctic Least Gray-Lake Whi te-
Date Code Set Fished Fry Smolt backs Char Cisco ling Cottid Trout Sucker fish
5-19-83 2 0000 1.0 19 0 2
2 0100 1.0 5 0
2 0200 1.0 4 0
2 0300 1.0 0
2 0400 8.0 0 0
2 1200 8.0 a 0
2 2000 2.0 1 0
2 2200 1.0 0 0
2 2300 1 .0 a a
5-20-83 2 0000 1.0 5 a
2 0100 1.0 10 0
2 0200 1 .0 7 0
2 0300 1.0 4 0
2 0400 8.0 1 0
2 1200 4.5 a 0
2 1630 4.5 0 0
2 2100 1.0 0 0
2 2200 1 .0 0 a
2 2300 1.0 9 0 2
5-21-83 2 0000 1 .0 4 0
2 0100 1 .0 7 0
2 0200 1 .0 4 0
2 0300 1.0 2 a
2 0400 8.0 0 1
NEWHALEN RIVER (RM-13) CATCHES, 1983
3 X 3-FOOT NET WEST Sheet 3 of 10
si te Time Hours Sockeye Sockeye Stickle-Arctic Least Gray-Lake Whi te-
Date Code Set Fished Fry Smolt backs Char Cisco ling Cot tid Trout Sucker fish
5-21-83 2 1200 9.0 0 C
2 2100 1.0 0 0
2 2200 1 .0 4 0
2 2300 1.0 4 0
5-22-83 2 0000 1.0 3 0
2 0100 1 .0 0
2 0200 1.0 1 0
2 0300 1 .0 0 0
2 0400 8.0 0 0
2 1200 8.0 0 0
2 2200 1.0 0 0
2 2300 1 .0 3 0 3
5-23-83 2 0000 1.0 3 0 1
2 0100 1.0 1 0 2
2 0200 1 .0 2 0
2 0300 1.0 2 0
2 0400 8.0 0 0
2 1200 6.0 0 0
2 1800 3.0 0 0
2 2100 1.0 0 0
2 2200 1.0 0 0
2 2300 1.0 3 0
5-24-83 2 0000 1 .0 6 0 3
2 0100 1.0 3 0 2
I I
NEWHALEN RIVER (RM-13) CATCHES, 1983
3 X 3-FOOT NET WEST Sheet 4 of 10
Site Time Hours Sockeye Sockej3 Stickle-Arctic Least Gray-Lake White-
Date Code Set Fished Fry Smolt backs Char Cisco ling Cottid Trout Sucker fish
5-24-83 2 0200 1.0 3 0 2
2 0300 1 .0 0 0
2 0400 8.0 0 0
2 1200 9.0 0 0
2 2100 3.0 6 0 1
5-25-83 2 0000 2.0 1 0 5
2 0200 2.0 2 0
2 0400 8.0 0 0
2 2100 1.5 2 0
2 2230 1.5 18 0 6
5-26-83 2 0000 1.0 10 0 7
2 0100 1.0 8 0
2 0200 1.0 10 0
2 0300 1 .0 2 0
2 0400 9.0 0 0
2 1300 8.0 0 0
2 2100 1.0 0 0
2 2200 1 .0 9 0 2
5-27-83 2 0130 1 .5 3 0 2
2 0300 9.0 0 0
2 1200 5.0 0 0
2 1700 4.0 0 0
2 2100 1 .0 0 0
2 2200 1.0 0 0
NEWHALEN RIVER (RM-13) CATCHES, 1983
3 X 3-FOOT NET WEST Sheet 6 of 10
Si te Time Hours Sockeye Sockeye Stickle-Arctic Least Gray-Lake White-
Date Code Set Fished Fry Smolt backs Char Cisco ling Cot tid Trout Sucker fish
5-30-83 0300 1.0 0 0
0400 8.0 0 0
2100 1.0 0 0
2200 1.0 0 0
2300 1 .0 3 0
5-31-83 0000 1 .0 10 0 1
0100 1.0 4 0 6
0200 1.0 12 0 3
0300 1.0 0 0
0400 8.0 0 0
1200 9.0 0 0
2100 1.0 0 0
2200 1 .0 0 0
2300 1 .0 5 0
6-01-83 0000 1 .0 3 0 4
0100 1 .0 0
0200 1.0 1 0
0300 1.0 2 0
0400 8.0 0 0
1200 9.0 0 0
2100 1 .0 0 0
2200 1 .0 0 0
2300 1.0 6 0
6-02-83 0000 1 .0 3 0
• J
i j I I , J I I I 1 r t ( t t J I I I I I , I 1 I ... I ,
NEWHALEN RIVER (RM-13) CATCHES, 1983
3 X 3-FOOT NET WEST Sheet 7 of 10
Si te Time Hours Sockeye Sockeye Stickle-Arctic Least Gray-Lake White-
Date Code Set Fished Fry Smolt backs Char Cisco ling Cottid Trout Sucker fish
6-02-83 0100 1.0 6 0
0200 1 .0 3 0
0300 1 .0 0
0400 1.0 1 0
0500 15.0 0 0
2200 1 .0 21 0
2300 1.0 3 0
6-03-83 0000 1 .0 13 0
0100 0.5 10 0
0130 1 .0 3 0
0230 2.0 0 0
0430 8.0 0 0
1230 8.0 0 0
2030 1 .5 0 0
2200 1.0 0 0
2300 1 .0 2 0
6-04-83 0000 1.0 3 0
0100 1.0 0
0200 1 .0 0 0
0300 1 .5 0 0
0430 7.5 0 0
1200 9.0 0 0
2100 2.0 1 0
2300 1.0 9 0
I I l
NEWHALEN RIVER (RM-13) CATCHES, 1983
3 X 3-FOOT NET WEST Sheet 10 of 10
Site Time Hours Sockeye Sockeye Stickle-Arctic Least Gray-Lake White-
Date Code Set Fished Fry Smolt backs Char Cisco ling Cottid Trout Sucker fish
6-16-83 0400 10.0 16 0
1400 7.0 0 0
2100 7.0 8 0
6-17-83 0400 9.0 0 0
1300 8.0 0 0
2100 3.5 1 0
6-18-83 0030 3.5 3 0
0400 8.0 0 0
1200 10.0 0 0
2200 2.0 2 0
6-19-83 0000 4.0 0 0
0400 10.0 0 0
1400 10.0 0 0
2300 9.0 3 0
6-20-83 0300 9.0 0 0
1200 9.0 0 0
2130 3.5 4 0
6-21-83 0100 3.0 0 0
0400 13.5 0 0
1730 3.5 0 0
2100 13.0 1 0
6-22-83 0000 4.0 0 0
NEWHALEN RIVER (RM-13) CATCHES, 1983
3 X 9-FOOT NET Sheet 2 of 2
Site Time Hours Sockeye Sockeye Stickle-Arctic Least Gray-Lake White-
Date Code Set Fished Fry Smolt backs Char Cisco ling Cottid Trout Sucker fish
5-23-83(a) 4 2100 1.0 0 0
4 2200 1.0 0
4 2300 1.0 38 1
5-24-83(a) 4 0000 1.0 181 9
4 0100 1.0 108 30
4 0200 1.0 47 109
4 0300 1.0 13
4 0400 8.0 0 0
5-24-83 3 2130 1.0 1 50
3 2230 0.5 0 0
3 2330 0.5 60 128
5-25-83 3 0030 0.5 170 67
3 0130 0.5 78 391 2
3 0245 0.5 31 20
3 0330 0.5 6 0
3 0430 7.5 0 0
3 2100 0.5 2 0
3 2200 0.5 0 0
3 2300 0.5 129 121
5-26-83 3 0030 0.5 240 3 6
3 0130 0.5 194 3
3 0230 0.5 95 7
3 0300 0.5 15 0
3 1530 2 0
(a) Operated from downstream cable; all other times are upstream cable.
• Fry
APPENDIX 2
LENGTH-FREQUENCY OF NEWHALEN RIVER (RM 13)
SOCKEYE --SPRING 1983
• Smolt
LENGTH-FREQUENCY OF NEWHALEN RIVER (RM-13)
(lengths in mm)
Date: May 16 May 16 May 17 May 17 May 17
Hours:
Gear:
Station:
20
21
22
23
24
25
26
27
28
29
30
31
32
33
34
35
36
37
38
39
40
41
42
43
44
45
46
47
48
49
50
51
52
53
54
55
56
57
58
59
Ave
2300-2230-
OOOO(a) 0000
IPT 3x9U
M(b) 3
2 4
2 5
(a) 0000 equals midnight.
0000-0000-
0100 0100
IPT 3x9U
M 4
3
2
3 11
3
(b) Located midriver--clownstream of Station 4.
(c) Actually about Station 3.5 due to gear failure.
2300-
0000
IPT
M
4
5
3
SOCKEYE FRY--SPRING 1983
May 17 May 20 May 30 June 8 June 22
0000-0100-0100-0200-0100-
0100 0200 0200 0230 0200
3x9U 3x9U IPT 9x9U 9x9D
2 3 M 3 4(c)
20
21
22
23
24
2 25
1 10 26
2 22 27
2 12 1 1 22 28
12 42 5 9 16 29
43 69 32 34 10 30
15 8 4 4 3 31
2 32
33
34
1 35
1 36
2 37
38
39
40
41
2 42
43
44
45
46
47
48
49
50
51
52
53
54
55
56
57
58
59
LEN\.iTH-r~RE\.lUENCY or HEWllALEN RIVEN. ( IIM-13) SOC~EYE SMOLT--SPRING 1983 Sheet 1 of 4
( lengths in mm)
Da te: "My 17 10 17 17 17 18 19 1~ 20 20 20 20 20 20 21 21 22 22 22 23 23 23
T1me: LlLluLI-2300-0000-0100-2300-0100-0000-2300-0000-0100-2200-1930-2100-2300-0000-0430-0400-1430-2300-0000-0100-0300-
~11 L10 0000 0100 0200 0000 0200 0100 0000 0100 0200 0300 2100 2200 0000 0100 1200 1200 2200 0000 0100 0200 0400
Gear(a): IPT 3x9U 3x9U 3x9U 3x9U IPT 3x9U 3x9U 3x9U 3x9U 3x9U 9x9U 9x9U 9x9U 9x9U 9x9U 9x9U 9x9U 9x9U 9x9U 9x9U 9x9U
Statlon: Hlb) J 4 3 3 H 3 3 3 3 4 4 4 4 4 4 4 4 4 4 4
60 60
61 61
62 62
63 63
64 64
65 6~
66 66
67 67
68 68
69 69
70 70
71 71
72 72
73 73
74 74
75 7~
76 76
77 77
78 78
79 79
80 80
81 81
82 82
83 83
84 84
85 85
86 86
87 87
88 88
89 89
90 90
91 91
92 92
93 93
94 94
95 95
96 96
97 97
98 98
99 99
100 100
101 101
102 4 102
103 2 103
104 104
105 4 15 II 105
106 3 7 10 6 10 106
107 8 4 4 3 107
108 13 5 10 108
10' 2 5 12 6 7 4 109
11(J 6 19 6 12 6 14 9 110
111 1~ 3 10 13 10 4 111
1 , ~ 4 8 10 9 5 6 15 4 112
11) ~ 10 6 7 8 4 8 5 113
114 13 6 10 114
115 15 8 6 115
116 9 4 2 116
, 17 8 117 ,," 2 118
119 4 2 119
120 '20
12 , '2'
122 122
, <) 123
124 , 24
125 125
126 126
,27 127
'28 128
'29 129
, ) 0 '30
, 3' 131
, ) 2 132
, J J 133 , ). , 34
la) Gear. IPT 1S 1ncllned plane trap; ]x9 is 3x9-foot net; 9x9 is 9x9-foot netl U ia upstrem cable, Dis down. trea. cable, aee text for other qear det.ai la.
Ib) M1dr1 ver locatlon--const.ant in study period and dovnst.rea. of cable at.ation 4.
LENGTH-FREQUENCY OF NEWHALEN RIVER (RM-l]1 SOCKEYE SMOLT--SPRING 198]
(length. In .Ift)
Sheet 2 of 4
Date, May 24 24 24 24 24 25 25 25 25 27 27 27 28 28 28 ,,8 28 29 29 29 3D 3D 31 31
Tae, 0100-0200-0400-2130-2330-0100-2100-2200-2300-0000-1200-2330-0030-0230-04]0-2100-2300-0]00-2100-2300-0000-2300-0000-0100-
0200 0]00 1200 2200 0000 01]0 2130 2230 2330 0030 1230 00]0 0100 0300 2100 2200 0000 04]0 2200 0000 0100 0000 0100 0200
Gear: 9x9D 9x9D 9x9D 9x9D 9x9D 9x9U 9x9D 9x9D 9x9D 9x9U
Statlon: 4 4 4 4 4 3 4 4 4 1
60
61
62
63
64
65
66
67
68
69
70
71
72
71
74
75
76
77
78
79
80
81
82
8]
84
85
86
87
88
89
90
91
92
93
~4
95
96
97
98
99
100
101
102
10]
104
105
106
107
108
109
110
II'
112
11]
114
115
116
117
llB
119
120
121
122
12]
124
'25
126
127
128
129
130
1]1
132
III
134
10
12
7
11
7
12
15
12
B
4
6
5
7
(c) one fish at 35 .m.
6
5
8
8
7
2
]
11
5
12
6
17
B
8
(el
9
11
7
5
6
2
4
2
6
18
6
5
6
2
2
1
6
4
3
5
15
5
'2
6
5
10
5
6
6
]
11
4
18
4
8
8
3
]
2
1
6
5
4
5
3x9U 9x9D 9x9D 9x9D 9x9D 9x9D 9x9D 9x9D 9x9D 9x9D 9x9D 9x9D 9x9D 9x9D
34444444444444
6
4
7
4
6
8
4
6
2
2
2
5
2
1
4
]
2 2
,.
2
6
2
5
1]
8
8
6
12
7
8
7
10
5
4
2
14
6
9
6
9
12
9
15
6
5
5
4
4
5
3
5
6
4
2
12
]
6
9
4
4
]
4
3
2
60
61
62
63
64
65
66
67
68
69
70
71
72
7l
74
75
76
77
78
79
80
81
82
83
84
85
B6
87
88
89
90
91
92
93
94
95
96
97
98
99
100
101
102
103
104
105
106
107
108
109
110
111
112
11)
114
115
116
117
118
119
120
121
122
123
124
125
126
127
128
129
130
131
132
133
134
LENGTH-FREQUENCY OF NEWHALEN RIVER (RM-13) SOCKEYE SMOLT--SPRING 1983
(lengt.hs in a ... )
Sheet. 3 of "
Dace: Hay]1 June 1 2 1 1 4 4 4 4 4 5 6 7 7 7 7 8 9 9 9 9 10
Tllle: 0200-0400-2300-0200-2300-2330-0030-0130-0330-2100-2300-0200-0300-0000-0100-0200-2200-2300-2200-0100-0300-2200-2300-2300-
0300 1200 0000 0300 0000 0000 0100 0200 0430 2200 0000 0300 0330 0050 0150 0250 2300 0000 2300 0130 0400 2300 0000 0000
Gear: 9.90 9.90 9x9U 9x9U 9x9D 9x90 9x9D 9x90 9x9D 9x9U 9x9U 9x9U 9x9U 9x9D 9x9D 9x90 9x9D 9x9D 9x9D 9x9D 9x90 9x9D 9x9D 9x9D
Suuon: 4 4 3 3 4 4 4 4 4 37 .3 3 5 4(d) 4(d) 4(d) 4(d) 4(d) 4(d) 4(d) 4(d) 4(d) 4(d) 4(d)
60
61
62
63
64
65
66
67
68
69
70
71
72
73
74
75
76
77
78
79
80
81
82
83
84
85
86
87
88
89
90
91
92
93
94
95
96
97
98
99
100
101
102
103
104
105
106
107
108
109
110
111
112
113
114
115
116
117
118
119
120
121
122
123
124
125
126
127
128
129
130
131
132
III
6
8
7
9
10
16
8
9
8
1\
5
I
4
13
4
2
4
4
4
10
3
5
10
5
19
1\
13
12
8
4
4
2
6
4
I
6
2
134 (e)
7
5
8
6
11
2
(dl Due co gear failure, 8t&t.lon 18 about. 1.5.
(e) One flSh at. 163 •••
4
4
4
6
4
12
Il
9
10
12
10
2
I
4
10
10
5
7
14
4
17
5
8
2
6
9
7
4
10
5
10
5
2
I
2
2
3
2
3
2
6
2
I
4
4
4
5
4
6
9
3
6
5
4
8
I
3
2
4
2
2
4
3
6
7
7
2
15
2
3
II
2
2
I
4
2
2
5
4
4
3
5
3
6
7
2
4
4
2
3
2
4
3
I
6
6
8
3
2
I
4
I
4
2
2
I
4
4
9
6
10
4
5
3
5
4
6
6
11
3
7
8
8
6
2
1
2
1
3
5
6
9
4
7
6
6
2
6
10
3
6
4
6
3
4
I
6
3
6
11
9
12
7
6
14
7
2
2
2
2
4
60
61
62
63
64
65
66
67
68
69
70
71
72
7J
74
75
76
n
78
79
80
81
82
83
84
85
86
87
88
89
90
91
92
93
94
95
96
97
98
9~
100
101
102
103
104
105
106
107
108
109
1\0
111
1\2
113
1\4
1\5
1\6
1\7
118
119
120
121
122
123
124
125
126
127
128
129
130
131
132
133
134
)ate: June 12
f1ae: 2200-
2300
Gear: 9x9D
Statlon: 4(dl
60
61
62
63
64
65
66
67
68
69
70
71
72
73
74
75
76
77
78
79
80
81
82
83
84
85
86
87
88
89
90
91
92
93
94
95
96
97
98
99
100
101
102
103
104
105
106
107
108
109
110
111
112
113
114
115
116
117
118
119
120
121
122
123
124
125
126
127
128
129
130
131
132
133
I ~
2300-
0000
9x9D
4(dl
8
2
6
18
2300-
0000
9x9D
4(dl
4
22
0000-
0100
9x9D
4(dl
134 If}
(t) One f11h at S2 •••
LDOGTH-f"REQUENCY OF N!:WHALEN RIVER IRM-ll) SOCKEYE SMOLT--SPRIIIG 1983
(length. in _I
Sheet .. of ..
APPENDIX 3
SOCKEYE SMOLT LENGTH AND WEIGHT DATA
NEWHALEN RIVER (RM 13), SPRING 1983
Time
Slide Gear/ Began
Number Station Haul
2
3
4
5
6
7
8
9
10
11
12
3x9U
3
9x9D
4
9x9D
4
9x9D
4
9x9D
4
9x9D
4
9x9D
4
9x9D
4
9x9D
4
9x9D
4
9x9D
4
9x9D
4
2300
2200
0000
0430
0400
2300
0000
2200
2300
0000
2330
2300
Date
05-15-83
05-20-83
05-21-83
05-21-83
05-22-83
05-22-83
05-23-83
05-25-83
05-26-83
05-27-83
05-27-83
05-29-83
Duration
of
Haul
1 .0
1 .0
1.0
7.5
8.0
1 .0
1 .0
0.5
0.5
0.5
0.5
1 .0
L
83
92
105
100
95
105
106
125
112
105
119
121
125
125
117
104
110
113
128
124
115
11 1
124
120
SOCKEYE SHOLT LENGTH AND WEIGHT DATA
NEWHALEN RIVER (RM-13), SPRING 1983
(scales taken for all fish reported)
Lengths (mm) and Weights (mg)
W L W L W L
420
560
850
765
678
873
880
140
1 , 110
855
1,300
1,256
1,445
1,460
1,265
815
1,032
1 ,144
1,670
1,445
1,060
1,005
1,490
1,285
128
99
101
65
112
115
109
112
98
119
132
80
115
114
116
110
127
123
113
76
125
753
833
179
1,075
1,110
955
1 ,155
723
1,257
1,715
385
1,170
1 , 1 40
1,340
1,095
1,525
1,360
945
325
1,500
83
98
104
87
112
112
116
110
115
105
121
97
88
82
115
124
102
112
88
115
720
841
480
1,100
1,220
1,025
1,203
806
1,440
700
510
425
1,248
1,475
700
1,065
360
1,205
102
102
105
95
121
126
103
124
79
109
114
91
113
86
W
710
827
878
855
132
1,435
872
1,555
415
970
1,135
646
1,105
505
L
80
80
92
80
112
118
108
120
80
118
113
94
105
85
W
390
378
577
375
1,045
130
1,120
1,330
395
1,245
1,070
760
500
Sheet 1 of 2
L
80
78
75
96
109
117
108
118
106
115
92
68
125
W
377
330
307
750
1,255
1,037
1,240
885
592
231
1,510
Time
Slide Gear/ Beqan
Number Station Haul
1 3
14
15
16
17
18
19
19
20
21
22
9x9D
4
9x9D
4
9x9D
4
9x9D
4
9x9D
4
9x9D
4
9x9D
4
9x9D
4
9x9D
4
9x9D
4
9x9U
3
2300
0200
0200
2100
2300
0000
2200
2200
2300
2200
2300
Date
05-30-83
05-31-83
06-03-83
06-04-83
06-04-83
06-07-83
06-07-83
06-08-83
06-10-83
06-12-83
06-15-83
Dura tion
of
lIaul
1 .0
1.0
1.0
1.0
1.0
1.0
1.0
1.0
1.0
1.0
1.0
L
115
112
133
91
90
103
112
86
119
115
109
122
107
105
111
119
104
114
95
123
114
SOCKEYE SMOLT LENGTH AND WEIGIIT DATA
NEWHALEN HIVER (RM-13), SPRING 19H3
(scales taken for all fish reported)
Lengths (mm) and Weights (mq)
W L W L W L
1,175
1,044
1,700
570
560
810
1,150
560
1,327
1,165
955
1,515
1,025
840
1,070
1,428
855
1,175
725
1,432
1,165
105
116
122
163
80
100
85
114
120
126
116
115
100
116
105
100
106
101
126
103
872
1,145
1,385
3,610
370
728
410
1,380
1,480
1,118
1,180
787
1,120
872
760
875
745
1,575
904
108
114
121
105
82
115
102
121
120
113
105
105
89
118
103
99
121
101
980
1 ,131
1,330
860
405
1,090
725
1,425
1,565
1,105
910
963
565
1,397
860
750
1,635
880
120
122
107
85
100
112
127
107
108
89
109
89
111
96
116
109
W
1,300
1,430
954
430
775
1,185
1,615
934
1,055
598
1,060
490
1,170
700
1,269
1,068
L
115
125
105
79
117
119
115
127
111
105
117
105
97
84
112
W
1,247
1,535
920
400
1,225
1,390
1,280
1,735
1,030
883
1,270
965
770
450
1,110
Sheet 2 of 2
L
115
95
102
96
107
119
115
101
105
113
117
101
101
W
1 ,117
675
810
725
905
1,312
1,220
818
935
1,185
1 ,210
850
APPENDIX 4
NEWHALEN RIVER AIR AND WATER TEMPERATURES
• USGS Gage House, OCtober 19, 1982 to March 16, 1983
• USGS Gage House, May 13, 1983 to June 23, 1983
• RM 13 West (Camp) Bank, May 15, 1983 to June 23, 1983
• RM 13 East (Tower) Bank, May 16, 1983 to June 21, 1983
NEWhALEN HYDROLOGY STUDY fACE 1
PREPARED BY DRYDEN & LARUE FOR DAMES & MOOHE
NEVHALEN RIVER -~AC~ HOUSE START TIME 09/3018~ 24 DO (NWGHOl.20DI
DATE TII'1E
---------------------
10/19/82 H:OO
10120182 Z4:00
10/2118224:00
;on2/8224:QO
lO/23/S2 2400
10/;:'U8224:00
101251B224:00
10126/<32 24:00
10/27/822400
10128182 24:00
10/29/B224 DO
10130/82 24 GO
10/31/82 24:0u
11/01132 Z·LOO
11/0<;/8224:00
11/03/822400
11/04/82 24Gu
11/05132 24 00
Il/06iB224 00
11107/822400
l1i05/B2 240G
11109Ja22400
11;10/82 240~
il/ili82 240ij
11/12132 H'OO
11/131822400
11/14/822400
il{i~ia2 2400
'WATER TEMP-DEG C
AVG
4.0
4.0
2.0
0.5
0.5
0.0
O.S
o. a
a .5
0.5
1 . Q
1 . 0
1 . 0
1 0
1 . :s
1 . 0
j
· 5
1 . 0
1 . 0
.0
i)
· :.
· 5
.5
.J
.lnN MAX
==== ====
3.:;
3. 0
1 . S
o. a
0.0
a 0
O.r
0.0
o. a
0.5
0.:;
0.5
0.:;
O. !l
.0
1 . D
1 . 0
1 . Q
1 0
0.5
0.5
1 . 0
0.0
O. 0
.0
1 . 5
1 . :;
1 . 0
.; . 5
4.5
3.0
1 . 5
0.5
0.5
0.5
0.:;
0.5
1 . 0
1 . a
1 . a
1 a
1 . 5
2.0
1 . 5
2.0
1 . ~
1 . ;)
2.0 . . .J
. .J
~ . 0
2.0
2. Q
2 0
2. a
AIR TEMP-uEC C *
Ave MI N flAX
=== ===
2.0 -1.5 4.0
-O.~ -4.~ 2.0
-7.0 -10.0 -4.5
-11.0 -13 0 -1.0
-11.5 -135 -8.0
-8.5 -13.0 -3.5
-6.~ -IIi) -3.5
-12.0 -14.0 -9.0
-7.5 -11.5 -3.0
-l.S -6.0 2.0
-10.5 -17.5 -S.5
-14.0 -18.0 -7.0
-3.0 -17.0 3.5
1 .0 -O.:j 3 5
-2.5 -5.0 -o.~
-8.0 -11.5 -::i.0
-12.0 -16.0 -7 5
- 1 5 0 -13.0 -11 :J
-1 3. J -160-10.5
-10 . 5 -17 ~ 0.:;
-0 ~ -4. :;
-3 0 -j.5
1 . 0
O. J
4.0 .5 -3.0
Lj -o.~
3 5 1 . :s
2.5 0 .)
-1;, -3.:S
-7,:> -IZ 0
.:t.v
~ 0
0.0
-;j (j
*winp. air temperature variations may in part be due to probe in sunlight.
NEVHALEN HYDROLOGY STUDY
PREPARED BY ~RYDEN & LARUE FOR DAMES & MOORE
FAGE 2.
29-JUL-B3
NEVHALEN RIVER -GAGE HOUSE
DATE THlE
----------------=====
11/16182 24'00
11/17/8224:00
1111818224:00
11/19/8224:00
11/20/8224:00
I1n1/8224:00
11122182 24'00
11123/822400
11/24/8224:00
1112::i/8224:00
11/2618224:00
11/2718224:00
1112818Z 24:00
11/29182 24:00
1113018224:00
12/01/8224:00
12102/82 HOO
12/03/82 2400
12104/82 24.00
12/0~18Z 24:00
121061B2 ::400
12107/82 24'00
12/GB18214 00
12/G9/a2 2400
12/10/822400
12/11/8224:00
12112/82 H:OD
12/13/82 24:00
1211418224:00
12/1:>182 24:00
12/161822400
12/17/B2 24:00
12./18/82 2400
12/19/82 Z4:00
12/20/82 24.00
12/21/132 24:00
12/22182 2400
12123/a2 2'lOO
12/2':;la2 Z4:00
12/2)/82240G
12/26/822400
12/27i82 2400
12/28/822400
lZi29/8224 00
12/30/82 24DO
12/31/82 24 00
01/01/9324:00
IJATER TEMP-DEC C
AVC MIN MAX
1 . 5
1 . 0
o . 5
0.5
0.5
0.5
o . j
1 .5
1 . 5
1 . 5
1 . 0
1 . 0
1 . 0
0.5
-3.0
-5.5
-0.5
0.0
o . 0
0.0
0.0
iJ ,)
o 0
o v
0.0
0.5
0.5
D.!!
0.0
-0 . J
-1.0
-0.5
-0.3
-0.5
-0 .5
-v.5
-0 . :'i
-1.u
-1 . 0
-0.5
-0 'j
0.0
[I . 0
O. 0
D.li
-0 5
-0 5
1 . 0
O.~
0.0
0.0
0.5
0.5
0.5
1 . 0
1 . 0
1 .0
0.5
1 . 0
0.5
-0. :i
-5.S
-7 0
-0 . 5
-0 5
-0. :i
-0 5
0.0
O. I)
-0.:;
-0 . 5
0.0
o 0
0.5
O. :i
-0 . 5
-O.:i
-1.0
-1 . 0
-0.5
-0.::5
-0.5
-0 . )
-1 .0
-1 .0
-1 . {)
- 1 0
-0 5
-0 . j
====
2.0
1 . 5
1 . 0
1 . 0
1 . 0
1 . 0
1 . :'i
1 . 5
2.0
2.0
1 . :;
1 . ~
1 . D
1 . 0
-0.5
-0 :i
o 0
o 0
0.0
0.0
0.0
0.0
0.0
0.0
0.5
1 . 0
1 . 0
0.5
0.5
-O.:i
-0 . 5
-o.S
-0.5
-0 .5
0.0
-0 . 5
-0 _ J
-1 . 0
-1 . 0
-0. !)
D 0
o I)
[; 0
O. 0 0 . 'J
-OJ 0 0
-0.5 -0.5
-0.5 -0.:;
5 TAR T TIM E 0 9 / 3 0 i 8 2 2':;: 0 0 ( N\J G HOI P D D )
AIR TEMP-DEC C
AVG MIN MAX
-11 . j
-13.0
- 1 7 . 0
-9. 0
Z.O
3.0
~ . 5
3.~
o . 5
2.5
- 3 .0
3 . 5
-0 . 5
-10 0
-zc. . 5
-Z 0 . !l
-21.0
-22.5
-14.5
3 0
3.0
O.S
-1.J
-4.5
-2.0
2.;;
1 . 5
-0.5
-Z . 0
-3 0
-7.0
-7.0
-9.0
0.0
1 . 0
-1 0
-14.0
-12 . :5
-10.3
O. :J
4.3
q 0
3 . 3
3.0
-2. 5
-3 0
-3.0
-13.5 -&.3
-18.0 -10.::'
-19.5 -14.:;
-16.Q 2.0
1 . 0 3 . 0
2.0
3. 0
-1 . :i
-2.G
-6. 0
-1 . 0
4.5
7.5 ... I. ,J
4 . 5
!l 0
3.0
7.0
-3.5 LO
-19.0 -J!i
-22.0 -18.0
-22.0 -19.0
-22.5 -18.5
-250-20.5
-22.0 -3.3
-3.5 6.0
0.5 5.5
-3. :i 4.0
-5.0 3.S
-~ 0 -G.::5
-9.5 3.0
-1.0 4.0
-1.5 3.5
-4 0 2.5
-7, 5 ~.O
-7.!l 2.0
-10.:; -:i:;
-14.0 -4.:';
-13.0 -6 ~
-7.0 Z.:J
-4.5 3.5
-9 0 3.:i
-17.0 -7.,J
-10.0 -10.0
-15.3 1.0
-z.:i 4.0
3. S 5 5
0.5 ::i.~
-1.0 b.5
-I . !)
-5. 5
-:i.0
-4. 5
:i :i
-1 . 5
-1.0
-1 .0
NEWHALEN HYDROLOGY STUDY
PREPARED BY DRYDEN & LARUE FOR DAMES & MOORE
PAGE; :3
29-JiJL-8~
UEWHAL~N RIVER -GAGE HOUSE
DATE TIME
----------------=====
111/02/83 24:00
01/03/S3 24'00
01/04/83 Z4:00
01/0S/S324:00
01/06iS324:00
01/07/S3 24:00
01 i08/83 24 :00
01109/83 24:00
1l1/10/S324:00
01111/8324:00
01112/83211.00
01/13/83 24:00
01/14/8324:00
01/15/83 24:00
il1/16/S324:00
01/17/83 24:00
01118/8324:00
01/19/83 HOO
01/20/8324:00
01/21/83 24:00
01/22/832400
01/23/8324:00
il1/24/8324:00
01/25/83 24:00
01/26/S324:00
01/27/S324 00
01/28/S3 24:00
01/29iS3 2400
01130/S3 24:00
01/31/S3 H'OD
02/01/8324:00
02/02/83 2.400
02/03/8324.00
02/04/832400
02/0:i/S3 24 00
02/06/83 24 00
02/07183 :4:00
02/08183 24:00
.)2i09/83 24:00
02/10/8324.Dil
02111/832400
02/1i:/83 2400
a2il3/d32400
02/14/8324:00
02/15/83 2<1:00
02'16/83 24:00
,J2/17i83 24 00
WATER TEMP-lJEG C
Ave
-0.5
-1.0
-0 . 5
o . 0
0.0
-1.0
-3. 5
-5.0
-7 5
-8. :)
-9. 5
-11 . 0
-11 . 0
-S . 5
-4.0
-3.0
- J . 0
-2.5
-1.5
-1.0
-1 . 0
-3.0
-4.0
-3.0
-2. . 5
-2..0
-2.0
-2.:;
-4 5
-4.0
-20
-1.0
-D.:i
-0 ~
-0 5
-O.S
-1 iJ
-1 . ~
-3 iJ
-~ 0
-5 a
-s 5
-6.~
-~ 0
-6 ~
-7 0
-f 0
111 N
-Ii. 5
-1.0
-1 . 0
-0.5
-0.:;
-2.S
11AX
-0 . j
-0. :i
0.0
O. 0
0.0
0.0
-11.0 -2.5
-6.0 -4.0
-8.5 -6.0
-9.0 -S.:;
-10.5 -8.5
-11.0 -10.5
-11.il -10.5
-10.S -5.~
-5 5 -3 0
-3.0 -2.;,
-3.0 -2.:;
-2. :5
-2 5 -1.0
-1 . :; -0.5
-1 . 0 -0 . ~
-Il . :; -1.0
-4.5 -<1.0
-4.0 -2.5
-2.5 -2.0
-2 0 -1 . S
-2.5 -l.j
-3.5 -2.0
-5.0 -3.5
-5.0 -3.0
-3 0 -1.5
-1.~ -0.5
-1.0 -O.S
-1.0 -il.5
-0.5 -0.5
-1.0 -0.5
-i!l -i 0
-2.0 -1.0
-3.) -2.0
-4.; -3.5
-!l.a -4.:i
-6.0 -5.0
-6.5 -6.0
-6.5 -6.0
-6:i -6.0
-7.0 -6.:-
-70 -6.:1
START TIME 09/30/S2 24:00 (NWGH01.POO)
AIR TEMP-DEC C
Ave
===
-5.0
-9.0
- 1 2 . :5
-IS.S
-26.5
-2 8. 5
-28.0
-27.5
-28.5
-22.5
-26 . 0
-2 7.0
-211.~
-0.5
-6 0
-17.5
- 1 4 . 0
-9.0
2.5
3.5
2.0
-9.0
-:j 0
0.0
-1.:i
-2.5
-2.5
-8.:;
-13.0
-1.5
1 . :;
2 . :;
2.5
1 . 0
0.0
-5.0
-6 0
-10 0
-17 0
-180
-19 i)
-Zl . :i
-£ 1 0
-19.0
-19.5
-19 0
-i7 ~
MiN MAX
===
-6.:i -of. 0
-10.5 -6.0
-16.0 -10.:;
-22.0 -16.:i
-29.5 -22.0
-29.5 -27.S
-29.0 -27 0
-29.5 -25.S
-30.0 -26.5
-27.0 -17.~
-28~ -22.0
-29.0 -24.5
-27.0 -21.:i
-21.0 1.:)
-18.:i 2.5
-2 ~ . j
-21.~
-23. J
1 . :i
3. 0
-6. 5
- i 8 . 0
-1 0 . )
-7.0
-7. =>
-1:i. 0
-17.~
- 1 0 . 0
-3 :i
-11 . :;
-12.:J
5
:1 . ~
4. S
~ . :)
2.0
.0
3.5
2 0
3.0
3.:i
-9.0
6.0
:i.0
1 . 0 5 0
-1.0 5:i
-0.5 j5
-z 0 1.:;
- 1 3 . :i 0 . 0
-lli ~ -2.0
-19.0 -4.5
-24.5 -9 0
-24.5 -11.0
-Z3.0 -12 (j
-i.7.0 -13.5
-28.5 -14 :i
-240 -9.0
-~q 'j -~.O
-: '5. U -7 :;
-23 ~ -9.0
NE~HALEN HYDROLOGY STUDY
PREPARED BV DRYDEN & LARUE fOR DAMES & MOORE
FAGt: I.j
29-JUL-i33
NE~HALEN RIVEh -GAGE HOUSE
IJATER TEMP-DEG C
DATE TIl1E
======== =====
02/18/83 2400
02/19/83 24:00
02/20/832400
02/21/8324:00
02/22/83 24:00
02/23/8324:00
02/24/831.400
02/25/8324:00
02/26/832400
02/27/83 24:00
02/28/83 :<:4.00
03/01/8324:00
0)/02/83 24:00
03103/832400
03/04/83 :<:4:00
03/05/8324:00
03/06/83 24:00
03/07/832400
03/08183 H:OO
0310918324:00
03/10/83 Z4:00
03/11/8324·00
03112/83 240(;
03/13/8324:00
03/14/8324:00
Q3/1:;/83 211:00
03/16/83 24:00
Ave
-7.0
-6.0
-'5.0
-4.5
-2. S
-1 . 0
-u.S
-0 . 5
-1.0
-0.5
-0.5
-0.5
-1 . 0
-1 . 5
-1 .5
-1 . 0
-1.0
-1.5
-2. 0
-3.0
-3.5
-4.0
-3.5
-3 0
-Z.O
- 1 . J
-1.0
MIN MAX
====
-7.0 -6.5
-6.5 -S.O
-5.5 -5.0
-5.0 -3.5
-3.5 -1.0
-1.5 -0.5
-0.5 -0.5
-0.5 -0.5
-1.0 -0.5
-10 -0.5
-0.3 -O.S
-0.5 -0.:;
-1.0 -0.5
-1:5 -10
-1.5 -1.0
-1.:5 -1.0
-1.0 -0.::'
-1.5 -0:;
-:;;'5 -1.5
-3.0 -2.3
-3.::' -3.0
-4 . 0 -.~ . ~
-3.5 -3.0
-3 0 -z.~
-Z3 -2Q
-2.0 -1.0
-:;;'0 -0.5
START TIME 09/301&Z 24:00 (N~GHOl.FOD)
AI R TEMP-DEC C
1.VG MIN MAX
-16.0 -19.5 -14 0
-10~
-13.5
-3.5
'L 0
2 " .,)
0.0
-4.0
- 5 .0
2. 0
-1 . 5
-7.0
-7.5
-0.5
2.!l
o .0
-7. 0
-100
-9.:J
-12.5
- 1 1 . :i
-,).0
-Z.5
-Z. 0
1 . 0
3.0
-14 0
- 1 ::; . 0
-13 0
O. 0
-2. :>
-8.0
- 1 :3 3
-0 . 5
-8.3
- 1 4 G
-1 :5 . '5
- i 8 . ~
-::; . 5
O. :i
-6.5
-15.0
- 1 9 . 0
-14 . ~
-17.5
-19.0
-11. 5
-7.0
-7, 0
-3.~
-6. 0
-.;.)
-Y.3
:i.~
7 0
::i.J
3.0
2.v
3 0
4 0
3.0
-v . ~
1 . 5
-1 .~
4 . (j
4 ::i
4. ~
2 0
4.0
-1.0
-3.3
-::, . 0
1 5
3.5
7 [)
1 0 . ::i
24.5
NEWHALEN HYDROLUGY STUDY PAGi 1
PREPARED BY D~YDEN & LARUE FOR DAMES' MOORE 19-JUL-83
NEWHALEN RIVEii -GAGE HOUSE START TIME Ci5/l3/S3 2'l:OD (NioIl:;OlPClD)
DATE TH1E
======== =====
0~113/83 24:00
05/14/83 24:00
05/15/83 H:OO
05/16/83 24:00
05/17/832oi:00
D~/lB/83 24:00
05/19/83 ;'4:00
OS/20/83,4:00
0~/21/a3 24:00
05IZZ/8324:00
05123/8324:0D
05/24/8324:00
OS/25/83 24'00
US/26/8324:00
OS/27/8324:00
OJ/,8/93 24:00
OS/29/83 ;'4:00
uj/30/83 24:00
0;'131/8324:00
06/01/83 2~:00
06/02/832400
06/03/133 24:00
06/04/~3 H:OO
06/05/a3 24DO
06/06183 1400
06/'7/133 :4:00
06/08/832400
06/09/133 24:00
06110/8324:00
06/11/83 24:00
06/12/832.40G
U6/13ii33 Z'; 00
06114/8324:00
G6/D/B3 24'00
Do/16/83 :::4.00
06/;7/03 2~GO
06/15/H ~.;O[;
16119/-33 Z';·OO
0612D/83 24 00
06/21/83 Z4:00
06/22/83 2,,-00
VATER TEMP-DEG C
AVG !'lIN MAX
::===
6.5
5.5
4.0
LO
6. Ci
6.0
6.5
1.0
6.0
6.~
6.Ci
7.0
7.0
6.S
1.0
7.0
6 . 5
7.0
6.5
6 . :i
1.0
6.5
6.5
/).5
7 .0
8.0
8.5
8. 5
9.0
8.5
0,5
8.0
5.0
a . u
d 'J
;
~.0
1 G
9 . 0
8.0
a.j
8 . 5
==== ====
4.5 8.:;
3.5 100
3.0 3. S
3. 5 1. 5
4.0 10.v
4.0 8.5
4.0 9.5
4 . 5 9. 0
a.3 7.5
5.:j B.:i
:i,j 6.~
j.O 9.5
5.0 10.0
:i.S 8.D
5.3 9.0
5.5 a.:i
5.:; 5.5
6.0 a ~
6.0 7.:;
5 . 5 7 . ~
6.0 8.5
6.0 7.0
6.0 7.5
6.0 7.5
6.0 8.5
6. :i 9. S
7.0 10.0
B.O 9.!i
B.il 10.5
B.O 9.5
B. 5 ~ . \I
7.5 9.0
7 . vB:;
.0 Q. il
7.0 So.O
rJ 10 . 0
-; ij 1 1 :;
7j 10.0
Sj 10 0
7 ~ ?O
i.O \oJ
7 5 ?O
AIR TEMP-DEC C
AVC
===
Y.Ci
8. \I
9.0
? . a
? . !i
6.5
10 . 0
6.0
6.!i
6.S
6.5
7.S
B.:i
? . 5
7 5
'f.0
1.0
0;..0
8. \)
9.5
8.0
8.5
1 2 . 0
12 . 5
12.0
11 . 0
11 . 5
9 0
11 . 0
10 . :i
9.5
10 . 5
11 . 5
12 . ~
13 . 0
1 1 . 0
12 . :i
1 1 . ~
1 1 0
1 1 0
MIN
6 . "
5.0
3 . 5
5.0
3. 0
0.0
-3. 0
1 0
2.0
4. \I
3. :;
o . ~
- 1 5
1 . 0
-1.3
-1.0
4. 0
6 0
5. :;
4 :.i
4 . 0
7.0
:;.0
~.
4 . (j
~ 0
6.u
4.0
- 1 0
7. 0
6.0
S.O
MAX
1 • -. .,)
1 2 . :i
8.5
1 3 0
12 . ()
1 2 . c)
18 . U
16.5
10. ~
11 . 0
10.5
1 Z . ~
l:i . U
12. :;
13.0
H.:i
1 ~ Q
1 2 U
11 . ::
1 1 5
,3 . ~
1 ~ . 0
11. G
1 e . ~
21 . 0
l~.S
17 . 5
1 II . 0
15.0
1::i . ~
15.0
:),~ 1!j.~
7. 0 19 . Ij
L5 ZO.S
:; i:l.S
7 . 5 1 3 . :i
8.:· 16.0
4 . .i 1 7 . 5
j 0 i 6 j
1 I) 12.5
NEWHALEN HYDHOLUGY STUDY
PREPARED BY DRYVEN & LARUE FOR DAMES & MOORE
NEWHALEN RIVER -WEST BANK
DATE TIME
======== =====
05/15/83 12:00
05/1~/83 16:00
05/15183 20:00
05115/83 24:00
05/16/8304:00
()S/16IB308:00
05/16183 12:0(;
05/16/83 16:00
05/16/83 ::000
u5/1<l/83 Z<l:OO
05/17/83 D4DO
()5/17/83 0800
05/17/83 12.DD
()S/17/83 16:00
05117/8320·00
OS/17/83 24.UO
OS/18/83 04:00
05118/83 0800
05/18183 1200
05/18/33 1600
OS/18/83 20.00
05/18/83 ':'1;00
05/19/83 04:00
ilS!191B3 08 00
05/1'1/83 12:00
,)S/19/8316:00
05/19/832000
:iS/l?/i33 2400
03/20/8304.00
05/20/83 08:00
OS/20/83 12:00
uS/ZO/83 1600
05/20ic320·DO
05120183 2400
05i21/83 04 00
D5/Z1183 08 00
03/<:1/53 12 00
051Z118316·00
05/21/832UOO
'i ~ " 2 1 " 8 3 ~ 4 . 0 0
0jl2i.183 04:00
1,.lATER TEMP-DEC C
AVe MIN NAX
3.0
3.S
4.u
3.:i
3.0
3.0
3.5
5.0
5.3
4.0
3.~
3.0
4.0
5 . ~
6.0
5.0
4.0
3 . ~
4.0
~.O
6 . :;
5 . ,
4.0
3.0
4 5
7 . 0
8.0
6.0
3.0
~.O
3 0
i Q
7 3
6
j 0
5 ij
'. ~
6 0
'5. [;
====
3.0
3.~
". .. .... oJ
3.5
j. Ii
3. 0
3.0
4.:i
5.0
3.5
~.O
3 0
3.0
4.:>
4 J
3.5
3 Ij
:; . 3
.s . 0
6.D
4 5
j.5
3.0
3.0
J . 5
7.0
:i.S
4.3
4.0
4.0
6.0
7 :;
6 . Ii
5 ~
5.~ .' ()
4.3
3.5
4.0
4.0
<j.0
j. 5
3.0
4.3
6.0
6.0
5.0
4.0
3 . :i
4.5
6. :i
6 . 5
:j 5
~.3
3.5
5.0
7. 0
7.0
0.0
4.3
3. 5
5.5
8. 0
8.0
? . 0
5.5
.; • Q
6.0
8.0
B.O
7 0
6.0
4 5
0.0
6.D
":i 5
J . U
F.liGE 1
29-~l1JL-a~
START TiME 05/15/83 1200 (NWWEDI.POD'
AIR TEMP-DEC C
Ave
7.0
6 . 5
i .0
6. 5
7.0
6. 0
10 . 3
12 . 0
10 . 5
7 . 0
S.U
~ .J
? . :;
9.5
'1.0
".s
3 . 5
5.0
S . :i
9.:i
9.3
3.0
-3.5
Q.D
10 . 0
14 . 0
16 . U
1 2 . 0
6.5
4 . 0
10 . 0
13 . 5
13 5
8 . :i
3.0
~ Q
7 5
d . :i
'( .0
~ 5
4.5
MIN
=:=
ci.3
0.0
6.0
6. U
6.5
S.O
7.5
11 . 0
\1.0
:i . ')
3. j
Z.:i
5. j
9. Ii
7.3
5.5
1 . 0
3. 5
7.0
a.s
8.5
-2.:>
-4. j
-!l.0
6.0
1 1 :)
14 . S
9 . 5
4.5
0.:3
8 0
1 1 . S
11 . ::;
.~ . 0
1 . 0
.; . 0
5.5
MAl.
===
i ;,
1 3 . 0
12.0
9 a
(I
6 0
9 0
1 1 . ii
11 . C> ....
, J
:; . 0
6.5
10 . [}
11 . 0
10.5
9.0
-i. S
12 . 5
17 . 5
18 . 0
16 0
8.j
9 (j
12.D
1:; 5
1:; . ~
1 1 ~
6 !i
6 U
" . 5
" G
.j
o . :i
5 U
NEWHALEN HYDROLOGY STUDY
PREPARED BY DRYDEN & LARUE FOR DAMES & MOORE
NEwHALEN RIVER -WEST BANK
WATER TEMP-DEG C
DATE TIME
----------------=====
as/22/83 08:00
05122/83 12:00
OS/22/83 16:00
OS/22/83 20:00
OS/22/83 24:00
OS/23/8304'00
05123/830800
OS/23/83 12'00
OS/23/B3 16:00
0::;123/8320:00
OS/23/83 2400
OS/24/83 04:00
as/24/B3 08'VO
OS/24/B3 12DO
u5/24/8316'00
05124/8320:00
aSI24/8324:00
OS/25/83 04:00
OS/25/83 08:00
05125183 1200
'J5125183 16:00
O::;/25/B32000
0512~/B3 24'00
05;26/830400
Q~IZe./83 08.'00
0512ol~3 1200
OS/26/83 16:00
05/26/S32000
05126/83 Z400
0::;/27/830400
v~/27183 08:00
0~127/83 1200
05127/83 16GO
OS127/83 20 .)0
0:>12718324 DO
0~12B/83 0400
u5/<:8/83 08:00
05128/83 12'UO
US/28/83 16:00
OS/28/8320.00
05128/832400
Ave
4 5
5.0
6. il
6.5
6.0
::;.0
4 . 5
5.0
s.~
5.5
S.:i
4.::;
'I . :S
5.u
7.0
8.0
eo . ~
::; 0
4 . 5
::.5
7 . )
8.::;
7 . 5
6.0
5. 0
S . 3
7.0
7 0
6. 5
5.")
6 . 0
a.U
.• J
~ ..
J . oJ
5.3
7 5
6 . ~
j-! r N
4.5
4.5
5.5
6.::;
S.:i
5.0
4.5
4.5
5.0
5.0
4.5
4 0
q.S
6.0
7.::;
S.5
4. ::;
4.0
4.:'
6.5
8.0
6.5
.. .., ".J
j 0
5.il
6. 0
7.0
~ 0
S.O
<I . 5
5 0
o
7 . J
6.0
5.0
~ .11
5.0
/) . 5
7.0
6.0
HAl
====
4. 5
5. J
6.5
6.5
5.5
~.Q
5.0
5.5
6.0
J.5
:; 0
4.5
,s.D
8.0
8 0
7.5
4.5
, ~ o ,;
8.::;
8.5
8.0
6.5
::i. j
6.0
.S
7.:;
7.0
0.0
i.v
7.0
a.o
8 0
7 5
6 . ~,
:i 0
6 :;
7 5
.0
PAGE Z
29 -JiJL-£< j
START TIME OS/1~/~3 1200 (NWWB01.20D)
AIR TEMP-DEG C
AVe. MIN 11AX
4.5
6.U
8.0
B.O
6.0
~.O
:>.5
7.5
9 0
8.0
4. :i
o . :;
Z.O
7.5
9 . :j
10 . ::i
~ . 0
-i..0
1 . 5
9.0
1 1 . 0
1 ~ . 0
8. 5
7.0
6. 5
9.5
10 . 5
'i.li
4 5
-2 :;
2.u
12 . 0
13 . 0
11 0
5.
-2. 0
1 . )
1 () . J
13 . 0
1 0 . 0
6 . j
4.0
0.0
7.0
J.:.i
3. :.
4.0
:;.3
8. 5
6. :;
2.:i
-1.0
-0.5
6. Q
8.5
9. 5
-1.:i
-j . 0
-t. 0
o. 5
9 5
10 . 5
6. 0
6 0
7.5
8. :l
8.5
- 1 . 5
-3. 3
-2.::'
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-Ii. 5
-3.0
-3.0
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1 1 . ..:
9.D
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:i.:.i
7 . :;
10 . 0
9.5
7. 0
5.5
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B 5
10 . 0
y 5
6.:i
3 . D
6.0
9 0
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1 1 . 5
1 i . 0
-1 . 0
6 . S
10 . 3
1 3 :)
13 (;
1 (] . 5
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7 . 5
12 . 0
1 Z . 0
10 I)
10 . 0
-1 . 5
8. Q
1 j . 5
16 . 0
i 1 . S
1 0 . ~
-0.3
7 . 5
12 . 5
13. j
1 j. . 5
8.5
NEWHALEN HYDROLOGY STUDY
PREPARED BY DRYDEN & LARUE FOR DAMES & MOORE
NEWHALEN RIVEk -WEST BANK
DATE TIME
======== =====
0~/2'i'/83 04:00
u!l/29/83 08:00
05129/83 12:00
O!liZ9/83 16:00
OS/29/8320:00
OSI29/8324:00
05/30/83 011:00
OS130/83 08:00
0~/30/83 12:00
0~/30/83 16:00
0:'/3018320:00
OS/30/83 Z4:00
0~/31/83 04:00
05/31/8308:00
05/31/83 1~:00
OS/31/B3 1600
05131/83 20:00
05131/83 24:00
06/01/83 0400
06/011330800
06/01183 12.00
06/01183 16:00
01)/01/83 20:00
06/01/8324:00
06/02/83 0400
06/02/83 0800
06/02/83 12:00
06/0.2/33 1600
06/0Z/8320.00
06/02/832400
06/03/83 Q4 00
06/0313308'00
06/03/83 1200
06/03/83 HOD
D6/c/3/8320'00
ti6/031B324 00
u()/04/33 04 OU
0/)/04/83 08 GO
06/0Q/83 1200
u6/tH/83 1600
00/04/83 ZO'OD
WATER TEMP-DEG C
Ave MIN MAX
5.5
S.5
6.0
6.5
7.0
6. :i
6.0
6.0
6.5
7. 0
7.0
0.:;
6.0
:j.S
6.0
6.5
6.5
1).0
.).3
6.5
7.0
6.5
5.5
5.5
6.0
7. ~
B.O
i . 5
6.5
6.0
() .0
6.0
6.0
j . 5
5 , 5
5.
5,3
6 . S
7.0
5.0
S. :;
6. :j
6.5
6.5
6.0
5. 5
6.0
7. 0
6.:'
0.0
s. ::;
5 " .J . .. ".J
6. :i
6.S
5 . :i
:i. 0
5.5
6.0
7.0
6.0
5,5
5.5
5.S
6.5
7.5
o
6.G
6.0
6.0
6.0
6.0
:j . 5
:5.5 -. oJ ....
~.O
6.0
5.5
6.5
6.!l
7 :;
7. a
6.5
6.0
7.5
7.5
7.u
6 5
0.0
6. 0
6 5
6. ::i
7.D
0.5
6.0
s.!)
6.0
7. 0
7.0
7.0
6.0
5.::i
6.5
~.O
8.0
B. 0
7.0
6.0
6.0
o. !l
6.0
0.0
3.j
5.:i
b. j
7.0
7 . 0
PAGE :;
Z9-vUL-83
START TIME D511~153 1200 (NW'''!B01POD)
AIR TEMP-DEG C
Ave; MIN MAX
11.5
0.0
10 . 'S
11 . :>
1 () . 5
a.s
7.D
il 0
9. :;
9. 0
8.:;
7 ::i
7.0
6.:;
9.J
10 . 0)
10 . 0
? . ~
6 . C!
l).oJ
8.;;'
10 0
8.5
6.0
3.::;
5.5
9.5
1 2 . 5
13 . :;
S 5
B.O
.5
8.0
S.O
8.0
. 5
6.0
b.il
&.0
9.0
9 . 3
3. :i
S.O
8.'S
)I S
8. :;
7.0
7.0
7. S
9 u
8.0
8.0
0.0
S. j
3.5
8.5
)I. 5
8.5
? . 0
S. 5
5.S
7.5
9.,)
8.0
3.:i
3.0
3.0
8.0
1 1 . :i
1 1 . 0
7.:i
fl.O
7.0
7.5
7 . ~
7.5
j,G
5 5
:i.a
7.0
8. ()
9.0
6.u
9 5
13.0
1 2 5
12 ::;
9.0
7 . 5
9.5
10 . 5
10 0
9 . C/
8.;)
8.0
8.5
10.0
11 . 0
11 . 0
8.)
7 .0
7. S
9.5
1 1 . 0
1 0 . 0
B.O
8.0
12.5
1 :.i . Ij
! 4 . 5
10 .
8 3
B.~
B.5
8.0
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7 j
.D
7 11
Y 0
10 . ()
i () . Ii
NEWHALEN HYDROLOGY STUDY
PREPARED BY DRYDEN & LARUE FOR DAMES & MOGRE
NEwHALEN RIVER -WEST BANK
VATER TEMP-DEG C
DATE 'iI?1E
---------------------
Hi04/S324'00
06/05/83 04:00
06/05/8308:00
06/05/83 12.00
06/05/83 16:00
06/05/83 20 00
06/05/8324:00
06/06/83 04'00
06/06/83 08:00
06/06/83 11::00
06/06/83 1600
06/06/832Q'OD
06/06/832400
06107/83 04:00
06/07/83 08:00
06/07/S3 12:00
06/07/83 16:00
06/07/832000
06/07/832'1'00
D6/D8iS304:00
06/08/8308:00
06/08/83 12:00
06/08/83 1600
06/08/83 20:0C
06106/832400
06/09/83 0400
06/091B3 08:00
0610 9 /83 12.00
06/09183 16:00
06/09/83 20.00
Jo/Q9/83 Zq:OO
06/10183 04.00
06110/8308:00
:)6/10/83 11::00
V6/10i.:33 16:00
06110/83 20.00
v6/10/832400
06/J1/83 D40G
06/11/830aoo
06/11/83 120(;
Ave
6 . 5
5.5
S.:i
6.0
7 0
7.5
7 a
6.0
5.:)
6.5
7 . 5
8.0
7.5
6.3
6 0
7. 0
B . :J
9.0
B.u
7.0
6.0
7.0
9.0
10 . 0
9. 0
B.O
7 5
8 Q
9 0
1i.0
';' 5
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~ 5
1 0 . (j
9 0
7 0
6 S
B.O
MIN MAX
6.0
5. :;
5. !i
5.5
6.5
"i.O
6.5
~.5
5.5
7.0
B.O
7 0
6.0
J 5
6. 5
8 0
8.;;
7.5
6.0
6. \)
6.5
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9.5
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7.0
7 . a
8.5
8.S
5
7.0
O.:l
/, . 5
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9 5
B. J
6.0
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7.0
7.0
6.0
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6.5
7. 0
7. S
7 . 0
6.5
6.0
7.0
8.0
8.5
8.0
7.u
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8.0
S.:i
7.5
6.:5
8.5
10 . 0
10. ;)
~ . :)
8.5
7.5
8. :;
9.:>
9.5
8.::i
7 . 5
7.0
9.0
1\). 5
10 . :;
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B 0
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t< 5
PAGE 4
H-Jlji.-83
START TIME 0511~/83 12 '00 (NWWBOl.POD)
AIR TEMP-uEG C
AVG
8.0
6.5
7.0
12 . 0
15 . 0
lo.J
13 . 5
<1. 5
14 . 5
18 . 0
19 . 0
13 5
7.0
B. 5
14.5
16 . 0
1:; . 0
9.0
-0.5
4.0
, 4 . 5
17 . 0
200
14 . 0
9.0
9 ~
12 . 0
1 3 :i
15 S
1 1 . 0
7.0
8.0
1 j . 0
1 3 . 5
15 . 0
a :i
-1 3
:j :5
1 ~ . 5
MIN
6.0
!i.:i
10. 0
12 . ~
14. :i
1 1 . 5
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1 . ~
8. 5
16 . !)
17 5
9.5
'1.0
4.:1
12. 0
14 . 5
13. 5
2 . 0
". 0
-2.5
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1 5 0
18. U
I 1 . 0
7.0
7.~
10. 5
12 . 0
14 . :;
6 a
6.0
i 0 ~
1 2 j
1 <i 5
1 a
-3. 0
-2.:5
1 ~ 0
HAX
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1 1 0
13.0
16 . :>
18.5
l:i . 0
11 . 0
a.~
17 . Q
20 a
~o 0
1 7 . 0
11. ii
1 2 . 0
16 5
1 7 :>
16 5
l<:i . ~
L. . 0
I I ~
17 S
20.0
21 . 5
1 a . 0
11 . ()
1 (j . j
14 0
1 6 . U
1 6 . :;
til . ~
8 5
1 1 . ~
1') . 5
l!i :i
16 . Ii
D.O
1 . Ii
i 2.0
13 S
NEWHALEN HYDROLOGY STUDY
PREPARED BY DRYDEN & LARUE FOR DAMES & MOORE
NEWHALEN RIVER -~EST BANK
WATER TEMP-DEG C
DATE TIME
---------------------
06/11183 16:00
06/1118320:00
Q6111183 24:00
0611218304:00
06112183 08:00
06112183 12:00
06112183 16:00
0611218320.00
06112183 2400
06113183 04:00
06113183 08:00
06113183 12:00
06113183 16'00
0611318320:00
u6113183 2400
0611418304:00
06114/8308:00
06/14/83 1200
06114183 16'00
06/14/83 ;:'000
06/14.183 24 00
H/D/B304'00
0611!)/83 08:00
06115183 12:0D
0611S/1l3 16:00
0611318320:00
1)6115163 24:00
0611618304'00
.)6/16/8308:00
06116183 12 CD
:)6116183 16:00
06/16183 2DOC
0611618324:00
0611il83 04'00
;)611718308:00
06117183 Ii; 00
,Jo117183 16:00
(,6117183 ZODD
06/171a3 24'00
06lItuB30400
Ave
9.5
Y . 0
8. 5
8.0
7.~
7.:;
B.5
S.5
8 0
7.5
7. 0
7.5
8.5
Y.O
8.0
7.0
6.~
7 . :i
a 0
d.:;
3.0
7 0
6.5
7.0
9 . il
9 . 5
a.o
7.0
o
7.0
a.s
;. . 0
8.0
7.0
6.5
i.S
. G
10 . 0
9 ,)
7 . 0
MIN
8.~
9.0
8.0
7.0
7.0
7.0
8.0
B.O
7.:i
6.5
0.5
7.0
8.:>
B.:;
7 5
6.3
6.~
/) . :i
7. ::i
B.::'
"7 . 5
6. :;
6.0
6.0
MAX
====
9 . :)
9.:;
9.0
8.5
8.0
B.O
9.0
8. j
8.5
S.O
7 0
B.5
9.0
9.0
8.5
7.0
7.5
Q.O
9.0
8 :i
1.5
7.0
B.O
8.5 10.0
8.:;
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7.0
6.5
6. :;,
~ 0
8.5
7 . 5
o.j
6 . 0
6.5
8.5
9.5
a 0
6.5
9.5
9.0
7.5
7.0
8.0
'~ . 0
9 5
8 5
" t I. ;)
'7 0
8.5
10 . J
i 0 . ::;
10.0
B.O
PAGE S
29-JUL-B,i
START TIME 05115/83 1200 lNIJ1JBOI POD)
AIR TEMP-DEG C
Ave MIN MA:<
13 . 0
11 .5
9.:i
B.O
8.0
1 1 . 0
13.0
12 . 5
9. :i
7 . Ii
7 5
13 . 0
13 0
10 . 5
8. (j
3. :i
6.5
125
1 1 'j
11 . :,
B . 5
7.5
7.0
11 . 0
13 . 5
1 I; . 0
10 . 5
7.S
8.0
1 Z . 0
i 1/ 5
14 . 5
10 . 0
2 . j
6 j
1-1. S
17 . 0
1 7 . ~
1 il.:i
1 . D
===
12 . 0
10, 0
8. :i
6. :i
6.0
10 . 0
12 . 0
1 1 . 0
8.0
3.0
4.0
11 . 5
11 . ~
10.0
4. ;j
3.5
J.S
Y.5
9. :i
10 . 5
~ . 0
4 . ~
0.0
9. 0
1 <l .i
13 . 0
1 0 :i
9.u
10 . 0
13 . U
1 4 ~
13 . 3
11 . 0
B.li
1 1 . 5
1 S . Ii
14 0
12.0
10 0
4 . J
9.5
14.5
13 . J
13 . 0
1 1 . 0
Y.O
9.0
1 3 5
12.0 14.5
12.3 13.3
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7. OJ 8 . J
? ~ 9 . ~
9. '3 14 . 5
lL:5 PO
12.0 IB.O
:i . 5 1 J :i
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16 iI 19:i
16.0 1:0.0
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-1 0 j . J
NEWHAL£N HYDROLOGY STUDY
PREPARED BY DRYDEN • LARUE FOR DAMES & MOORE
NEWHAL£N RIVER -WEST BANK
WATER TEMP-DEG C
DATE 71l1E
---------------------
H/18/83 08:00
06/18/83 12:00
H/lS/83 16:00
06/1S/8320:OO
06/1S/83 24:00
06/19/8304'00
06/19/83 08:00
06/19/83 12:00
06/19/83 16:00
06/19/83 20:00
06/19/S3 24:00
06/20/830400
00/20/830S:00
o6120i83 1200
06i20/83 16.00
o6n0/8320:o0
06/20183 Z<1:00
06/21/83 0400
Q6/21/83 08:00
06/21/83 1~ 00
06121/83 16:00
06/21/83 2.000
,j6/21/B324:00
06122183 04:00
06/ .. Z/d3 08:00
06/22/83 1200
tj6n2183 16:00
06/22/83 20 DC
u61ZZ/83 Z4 00
OblZ3183 04 00
,)6113/830800
AVG
====
6.S
B.o
10 . ~
11 . 0
10 . 0
8.~
7. 5
S.O
9 . ~
9 .5
8.5
8 0
8 . j
9.5
Y.5
s.)
8.0
7.u
7,5
7 . ~
o ~
7.S
9.11
So 5
9 0
8 0
5
i1 I N
0.0
7.0
9. 0
1 1 . 0
9 0
7.S
7 . a
7.J
8.:i
9.0
8.:1
8.0
7.5
8.0
9.0
9. ij
8.S
7.0
7.0
7.0
8 D
9.0
a. a
6. S
6.5
7.u
S 5
9.0
a 5
8 0
flAX
7.0
9.0
1 1 . 0
1 1 . J
1 1 . 0
Y.O
.., ..
I. oJ
9.0
9 . ~
9 S
9 . 0
8.S
8.5
9.5
9.!i
10 . 0
9 0
8.5
7.~
B.O
9. :i
9.5
9.0
8.0
7 . 0
8 5
9.S
9 :;
? 5
a 0
PAGE 0
21-JUL-8:;
STAfiT TIME 0~'1~/83 12.00 CNWWB01 POD)
AIR TEMP-DEG C
AVe:. t1IN HAX
===
~ o'
J • .J
13 . 5
1 S . 5
18.5
12 . :;
8 .0
9.0
11 . 5
12 . 0
11 . 5
10 . 0
9.0
10 . ~
13 . 5
14 . D
13 . 5
10 . 5
5.0
5.~
13 . 0
15 . 0
13 . 3
1 0 . ~
3.5
6.S
13 . 0
14 0
13 . 0
1 1 J
10 . 5
10 . 5
-0.5
12. J
18 . 0
16 . 0
9 0
6. 0
7 . j
10. J
1 1 0
10 5
? . 0
8.0
9. :5
11 . "5
1 3 . ~
12.0
8.0
2. . 5
2 . :;
Y.5
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12. 0
6 . :i
1 . :>
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11 . S
1 2 . ~
1 Z 0
11 . 0
,. '3
10 . 0
1 Z 5
18 . v
1 9 :i
zo.o
16 0
10 . 0
1 1 . 0
12 . 5
13 . 0
12. . CI
1 1 . S
10 . 0
12 a
15 . 0
1::; 0
14 . j
13 . 0
9
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16 . IJ
13 5
12 .
0.0
1 Z 0
14.0
1 ~ I)
13 . 0
12 S
11 . 3
1 1 . 0
NEWHALEN HYDRULOGY STUDY
PREPARED 51 DRYDEN & LARUE FOR DAMES & MOOrlE
NE~EALEN RIVER -EAST EANK
'WATER TH1P-!)EG C
DATE TIME
---------------------
05i16/83 1000
05116/83 20 OU
05/16/83 24:00
0:;/17/83 04:00
05/17/8308:00
05/17/83 12:00
05/17/83 1600
05/17/83 2000
05/17/B3 24:00
Oj/lB/S30400
05/18/33 (·8:00
05/18/83 12:(10
05/18i83 16:00
OJ/18183200o
05/18/832400
03/P/82 0400
J5/Pie3 08:00
05/19/83 1200
,)S/19183 16:00
05i19/83 :;:<)00
QS/19ta3 24:00
05/20/83 04'00
05/20/B3 08:00
05/20/83 12:00
OS/20/83 16:00
05/20/83 2000
05/20/B3 24:00
05/~1/83 (;400
05121/830B'GO
OS/21/B3 1: 00
05121!O3 1600
Q~1211B3 20 00
u5121/B3 2400
0'j/2~/83 0400
OS/2:;83 GaGO
05/22,83 12;)0
05122/82 1600
05/2118~ 200D
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2 ~-.j·I)¥..-8:'
START TIME 05116183 1600 CNWEEOI.FOD)
AIR TEM?-C1EG C
AVG MIN !~A;{
I Z . 5
1 D , :>
7. D
3.0
4.0
.., ~
I . ,J
1 1 . 0
10 . 0
6. :>
3.D
.~ 0
10 I)
1 0 Q
3 , :>
-2 5
0.0
9.0
14 . 5
1/:1 0
12 . 0
6.;)
4,0
10 . '3
14 , 5
14.0
8. S
3,0
4.5
7.S
8 , 5
7 ()
~ 0
4 0
4.5
6 . :.
~.O
8.5
S . 5
1 I . 5
s.}
3. 5
2 :i
5.5
5
7,5
~ . 5
... L , ,J
3. J
1 4 .)
I ~ [.
B .
1 L . 5
I? •
7.5
4 .• '
6.il
6.:' 11.0
9.0
,. j
-2.0
-3. '3
-3.0
4.5
I 2 . 5
! 5 . 0
9 5
4. J
I . u
S.5
1 2 0
1 1 . 5
J . 5
1 , 0
Z . 5
I> . 0
7 0
6. :;
';.5
4.0
4 . v
1 I . 0
11 3
9 . 5
-1 . 5
4.5
12 . S
16 . 0
17 , :.
B.O
8.5
13 , G
16 . 5
16 . {j
1 1 , ~
1 0 :.
1 Ij . U
? (i
6.3
4.5
o
9 !j
~ 0 I 1 0
o 1 0 .
~ 5 0
NEVHALEN HYDROLOGY STUDY
PREFARED BY DRYDEN & LARUE FOR DAMES & MOORE
NEVHALEN RIVER -EAST BANK
DATE TIME
========
OS/23/830B:00
03/23/B3 12:00
0!l/23/83 16:00
OS/23/B32000
OS/23/83 Z4:00
OS/24/83 04:00
OS/24/B308:QO
OS/24/83 1200
OS/24/83 1600
OS/201/83 ZOO!)
OS/24/83 24:00
OS/25/B3 04:00
u5/25/83 08:00
OS/25/83 1200
051Z5i83 16:00
05125/8320:00
05125/83 24:00
051Z6/83 04 00
-)5126/8308'00
OS/26/83 1,,:00
05i26183 16:00
05120/8320'00
OS/26/83 2400
OJ/ni83 04:00
0~/17/83 08:00
05127/S3 12:00
OS/27/83 1600
05 1 2718320:0(,
u5/27:832400
,J5/28/83 04 00
,j5/Z8/83 0800
05128/83 1200
0SIZ8/83 16:00
OS/28/83 20:00
J5128/83 Z4'00
0:'/29/8304'00
OS/Z';.1330800
03/29/33 22Q>J
05129133 16JO
li5/29/S., n'OD
,)5/29183 2400
\.lATER TEMP-DEG C
AVG MiN MAX
====
S . 5
:; . 5
6.0
6.0
6.0
5.5
5 . :i
:; . 5
7.0
8.0
7 0
6.0
5 . 0
5.5
? S
B . 5
7 . :J
6.0
5.5
0.5
7.0
7.0
6.0
5.5
6.0
7.
8.0
7 0
6.0
'j . 5
6.0
i.O
7 5
7.0
6.D
~ . 5
6 0
6 . 'j
! . 0
7 0
====
5.5
5.5
:i. ::i
6.0
5.5
5.5
:':1.5
5,:;
6 .• )
7,5
6.5
:s.~
5.0
:; 0
6.5
B.O
7.0
5. S
5 .
j.S
6. 0
7.0
6 . :i
~ ..
.J . .J
:i . 5
" . .J . .J
7.0
1.5
6.5
j,5
S . 5
.).5
6 S
7 5
1i.5
s. j
;'.5
6.0
~ . :i
b.j
6 :i
S.:i
6.0
6.0
6.5
6.0
6.0
S.~
6.5
7.S
8.0
7 5
b.:i
5.5
6.5
8.0
& . j
8. 0
7.0
5.5
6.0
7.0
7.5
7 . 5
6.5
5.5
7.0
B.O
8.0
B.O
6.5
5 5
6.5
1 . j
7 5
7 ~
e. '5
6.0
t .J
7 5
7 " .\)
PAGE 2
Z9-J'H-&3
START 7I11E 05116ia3 16:00 (N1J£BOl.E'OD)
AIR TEMP-DEG C
AVG MIN MAX
:i.0
7.S
9. j
7.S
4.5
1 . 0
Z.O
7.S
10.0
11 . 0
4. l
-1.5
I . ~
9.0
12 . 5
1 j . '5
B.O
6.5
6.5
10.0
I I . 5
9.5
-1 . Q
2.5
10 . 5
13 . 0
10,j
0.0
-1 . 0
2 . )
1 D . 5
1 3 5
1 1 . 0
7 ,J
5.0
5 . 5
9.S
1 I . ~
1 1 . 0
8 0
===
4 . :i
5.5
a.o
3.5
3.0
\I 0
0.0
:; . 0
9.0
9.5
-0 . 5
-2. 0
-0 . .i
6.0
1 1 . 0
10 :;;
7 0
~. ii
j )
7 5
o . :j
a. ~
10 5
~ . 5
:; J
~ . \)
:i . Q
Y . 3
I I . ~
11 . j
10 0
-0. j
5.5
11 . S
1 Ii . 5
1 4 . 5
1 0 . 5
7 . Q
.5
! 3 :;
ij l'l 0
a . oJ 1 1. . D
-l.u 1C,0
-z . Ci U :;
-0.5 6.5
6.3 14.5
9.0 l!l.S
8 . 0 12 . 0
O.~ 10.5
-1.iJ i 0
., D 1".:;
d.G l:i.:i
9 5 13 0
j 0 .. Q
1. 0 . 5
5 <) . 5
!< . 0 13 . U
9. ~ 125
I; 0 1 ~ :,
7 a 9 . Q
NEWHALEN HYDROLOGY STUDY
PREPARED BY DRY~EN & LARUE FOR DAMES & MOORE
NEWHALEN RIVER -EAST BANK
DATE TIl1E
----------------=====
OS/30/83 04:00
05;30/83 0800
05/30/83 12:00
05130183 16:00
Ojl30/83 2000
05/30/83 2'1'00
05/31183 04'00
05131/8308:00
05/31/83 12:00
Q5/31183 16:00
Oj13118320:00
05131/83 Z400
06/011830400
06101/8308.00
06/01/83 1200
06/01/83 1600
06101/83 2000
06/01/8324:00
06/02/83 0400
V6102/83 08:00
06/02/83 12.00
00102/83 16:00
06/02/8~ 20:00
06/02/83 2·LOO
06/03/B304'00
li6103/830S'00
06/03/83 1200
06103/83 1600
06103183 BOO
06103/83 24:00
06/01118304.00
u610-l/83 0800
06104183 1200
,)6101i/83 16'00
u6/04i83 20'00
u6lli"/a3 2400
06105/83 0400
061051830il':OO
,)6105/83 1200
utIO:i/a:; H:OO
06/05183 20'(li)
WATER TEMP-DEC
AVG MIN
6.5
6.0
6.5
1.S
7.0
O.S
6.:;
6. 0
6.5
6.5
6.5
6.5
6.0
5 . ~
6.0
6 5
7.0
6 5
0.0
6 0
6.0
1.0
8.0
7.0
6.5
6.5
6.5
6.5
6.5
6 . ,)
6.0
0.0
6 0
6 . 5
7.0
6 5
6 0
7.0
6.0
6.0
6 I)
7.0
7.0
6.:3
6.5
6.0
6.0
6.~
6.3
6.0
5.3
5.::i
6.0
6 . 0
j S
6 .0
6.5
7.'3
6.5
6.:;
6. :i
6 . '3
6.S
6.0
6 . 0
:; • ..J
6.0
6.0
'? U
6.0
6 0
e . 0
6 :.i
7.0
C
MAX
6.'3
6.0
7.~
7 . 5
7.5
?O
6.0
6. :;
7.0
7 0
6 . ~
6.0
5.5
6.0
7.0
7.0
7 . G
6 II
6.0
6.5
7.5
8.0
7.5
6.5
6.~
6.5
6.:5
6.S
6 . :i
I) . G
6 . 0
7.0
7 0
0.0
6 5
.0
7.u
PAGE 3
i.9-.J1JL-83
STAHT TIME 05/16/83 10:00 (NWEBOIPQDJ
AIR TEMP-DEG C
AVG MIN MAil
6.5
7.:i
10 . 0
9.0
8 . J
7 . 0
7.0
7.0
If . 0
10 . 5
10 . 0
6 j
5 5
6.0
B.5
10 . ~
1f.0
6.0
3.5
:j :.i
9.:;
1 2 . 5
13 . :;
S.5
8.0
7.0
7.0
7.:1
B.O
Q
5.0
~ 5
B.O
10 . D
B.G
6 :.
7 0
1 ! . ~
: 5 0
16 . :;
===
6. 5 7 (i
6.~ 9 j
9.j l1.u
7.~ lOG
8.0 y(;
6.0 a.s
5. J 8.5
4 0 B.!>
a.o 10.5
r ~ 11.5
8.0 12.0
6 0 8.0
q . 5 6 . D
:i.07 0
7.0 10.0
9.S 12,0
7 . '3 10 . 5
3.5 B.O
3.0 4.0
35 S.O
? .:; i 2 . :;
12.0 111:3
ID.v 14.5
7.3
7 . 0
e . 5
7.0
7 . 5
4 . ;;
4 5
7 D
8 . oj
8 5
8. Q
7 . ~
8 0
? j
? Ij
i G
&.3
10 . ~
.:.5 0.5
J 5 i 0
& 5 13.:;
13.5 .70
1:' . 0 j ~ 3
NEWHALEN HYDROLOGY STUDY
PREPARED EY DRYDEN & LARUE FOR DAMES & MOORE
NEWHALEN RIVER -EAST BANK
DATE TIME
---------------------
06/06/83 04:00
06/06/83 08:00
06/06/83 1200
06/06/83 16:00
06/06/83 20:00
06/06/8324:00
06/07/83 04:00
00/07/8308 ao
06/07/83 12'00
06/07/83 16:00
06/07/8320'00
u6/07/83 Z4'00
06108/83 04'00
06/08183 08:00
06/08/83 12:00
00/0.3/83 16:00
06/08/83 20:;)0
06/08/832q·00
06/09/83 0400
D6/09/83 OB:OO
061091B3 1200
116/09/83 16:00
06109/83 20'00
u6/Q9/B324:00
06/10/830400
00/10/8308:00
06/10/83 12:00
1l6/10/B3 16:00
D61lD/S3 20 DO
06/10/83 240·j
06/111830<\'00
li61l1/83 08:00
06/11183 1200
'Jo/I1/B3 1600
0611119320:00
U6dli33 24'00
06/12183 Oq DO
ij~112/83 08.va
06112/83 1:00
VATER TEMP-DEG C
AVe MIN J1AX
====
6. 5
6.0
0.0
o . :;
7. j
&.0
7. 5
7 .0
6.S
7.0
8.0
8 . j
8 0
7.:i
6.:5
7.5
8. :)
9.5
9.0
8.5
5. 0
8.0
<3.5
9 .0
8.5
8.0
S.V
&.0
9 . :i
10 . 0
• 0
B . 0
7 5
B.O
9 0
9.0
9.0
B ~.
6.0
6.0
6.0
7.0
7.3
7.0
6 . :;
6.:i
6 5
7 5
S,j
7 :i
7.0
6.5
6.3
8. 0
9,5
B 5
B.O
8.0
8. Ii
8.0
8.5
a. 0
8.0
7 5
S.O
8.5
9 ~ .. .J
a s
7.5
i 5
7.~
3 :i
9 0
d 5
~
, :i
B.O
7.11
6.5
6.0
7 . 0
7. 5
8.0
8.0
7.0
6.5
i . 5
8.5
9 0
8.!>
7. j
7.0
8.0
"9. S
9.5
9.5
8. :;
8.0
8.5
9.0
9. 0
8 . S
S.O
8.0
8.5
10.0
10 . 0
9 5
B.5
9.0
&.5
'f 0
o
8 5
B . j
8.5
?AGE II
29-Jij'i,.-d3
START TIME 0!l116/83 1600 (NWEBOI POOl
AIR TE:1P-DEG C
AVG
13. :i
6.5
4.0
13 . D
t 7 . 0
18 . 5
13 . 0
7.5
B 0
13 . 5
16 . :i
16.0
r 0
0.5
3 :i
13 . 5
18 . :)
1 9 . 0
14 0
9.0
10 . 0
12 0
14 . 5
11 . 0
7.S
7.5
1Z . 0
1 q . )
1j. :;
3.:l
-0 . 3
4 . 5
12. 5
14 0
12 . ()
9.0
.., ~
I . .J
a.5
1 1 . ;,
MIN
10.0
LO
Z 0
i. 5
1 J . 0
16 . 5
a.5
6.0
4.5
10. ~
1 !l . j
1 4 . 0
3.0
-1 . 5
-1.0
9. ;,
16 5
17 . 0
1 Ii ()
o
a c
8.5
i 1 . Ii
13 . 0
8 . 5
5.S
6.0
10. 0
1 3 . :i
1., . 5
-1.5
M.U
1 :5 . 0
1 1 . 0
7.:;
15 3
19.0
1 9 . 0
16 . !)
10.0
1 J . 0
15.5
18 . 0
17 . J
14 . :i
2 .• '
9 . :i
16 . ~.
i 1 5
:;;0.5
1 7 . 0
1;:. Ci
i 0 J
12 \j
14 . 5
15 . D
1 q . 0
9.U
9 . ::;
14 . D
1 5 . J
16 . j
1) 0
.J
-j;; ll.~
11.5 14.0
ik 0 l~j
9:; 140
a.o 10.0
6 ~ 8 . 0
o J 10.0
10 0 1:; . 0
NEWHALEN HYDROLOGY STUDY
PREPARED BY DHYDEN & LARUE FOR DAMES & MOORE
NEWHALEN RIVER -EAST BANK
DATE TIME
======== ====:
06112183 1600
06/12183 20:0u
06/12183 24:00
06/13/8304:00
06113183 08:00
06113183 12:00
136113/83 1600
06/13183 20:00
06113/83 2400
06114/8304:00
0611418308:00
06114183 1;;:00
06/1'l183 1600
061141832Ci OU
iJ6114183 24:00
061151830400
06115183 08:00
06115/83 1200
06/15/B3 16:00
06115/832000
v6/15/83 24:(j0
06/101830ilOu
06/1618308:00
06111>1&312:00
06110183 16:00
06/16163 2000
G6/i6/83 24'00
06/17183 0400
06,'17/83138:00
O~117/93 12:00
06117183 1600
06117163 20'00
06/17183 2400
061181830400
06/18i830300
D6:18183 !2Qu
V611aiB31600
06/1&18:; 2.0 00
061181832400
IJATEH TEMF·-DE(; C
AVe MIN MAX
8 . :i
8 :i
8. :i
8.0
7.5
7.5
8.5
8.5
8.0
7. os
7.0
7 j
8 0
8.0
8.0
7.5
7 0
7.0
a 0
8 ;;
a 0
7.0
7 . u
B.O
&.5
8. 0
7.5
7.0
7.0
d.5
9.3
a.'l
7 J
8 . 0
~ 3
1 1 . 0
10 . 0
8.5
8.5
11 . 5
7.5
7.5
7.5
11 .0
8.0
7. 5
7.0
7.0
7.0
7 . ~
8.0
7 :>
'i .0
? . Q
7.0
8.5
7.S
7.0
6. 5
6. :;
7. :i
8.5
11 . 0
7.0
7.0
7.0
8 . 0
9.0
B.O
7.0
Q
I.J
1 D . :;
====
9.0
9.0
8. :i
8.5
8.0
8.0
8. S
8.5
8. 5
7.3
7. 0
7.5
8.0
Es 3
B.O
7 0
7 5
8. :i
9.0
a . 5
7.S
7.0
7.5
8. :i
8.5
8.:>
8.0
7 5
a . D
9 0
9 j
? . 5
8.0
g 5
1 il . 5
1 1 . 0
Q 0 1 1 . 0
8 0 9 u
::' AG E :3
29-Jlji.-5~
START TIME 05116153 16 00 CNWEBOI POD)
AIR TEMP-inG C
A V G ;11 N ~l Ai(
===
13 . 5
12.5
9 0
7.0
7.0
1 Z . 0
13. 5
10.5
SJ.O
4.0
6. 0
1 1 j
1 Z 0
12 . 0
8. J
7.3
7. 0
1 D . :;
14.0
14 . 0
10 . 0
8.v
3.0
1 1 . 3
14 . 5
14 . 5
10 . 0
3.j
6.0
1 3 . :;
1 7 . 5
18 . :i
10 0
2.0
5. 0
14 j
1 9 5
1 2 5
9.5
1 2 5
11 . 0
7. 5
:) . 0
4.5
10. 0
1 2 . ~
9. 5
:5 0
4.0
a. 3
8 . 5
10. :)
5.0
S. 5
5.5
8.5
12. 5
12. S
8.:)
7.0
6 5
9.5
to. 0
1 0 . S
:i.J
Ii 5
1 6 S
1 0 . 5
4.0
\/.:i
.) ~
10 5
18 0
===
1 1 . 0
& . 0
10 . il
14.5
H .0
12 [;
9.5
5.0
8.5
13 . 5
J.:j 5
14 . 0
1 1 . 0
8.5
9.0
13 . 0
16.0
16.0
12 . :i
8.5
9.:i
14.0
16.0
17.0
13 . 5
5.j
10 . v
1 a ()
1" a
20 . 0
1 6 . 5
3.5
1 0 . !l
1 & 5
20.::!
6::; i 0 . 5
NEwHALEN HYDROLOG'l STUDY PAGE 6
FREPARED EY DRYDEN & LARUE FOR DAMES & 1'1OORE H-JvL-&3
NE\.lHALEN RIVER -EAST BANK START Ti l1E OS116/B3 1 .~ : 00 (N\.lEB01.POD)
\.lATER TEMP-DEC C AIR TEMP-DEC C
DATE TII1E AVe MIN MAX Ave 11! N MAX
-------------------------------=::= --------
116/19/83 08:00 7.5 7 .5 8. 0 9.0 7. 0 1 0 . :,
06/19/83 12:00 Ii.O 7 . . 8.5 11 . j 1 0 . Q 12 . :i -'
06/19183 16:00 9. 5 8. 5 9.5 12 . 5 9 :j 14 . 0
06119/83 20:00 9 ~ 1.0 9. :i 11 . 0 9. 0 12.0 .oJ
06/19/83 2<1:00 ... 0 9. 0 9. 0 1 0 . 0 9.0 i 1 . !)
06/20/83 04:00 9.0 8. j 9 0 B 5 7 . 5 Y.5
u6/Z01B3 08: 00 8.5 8 5 8.5 10 . 0 8.S 12.0
06/20/B3 12: 00 8.~ 8 j 9.0 1 :; . j 12 . 0 16.0
06/20/83 16 . GO 9. 0 9 .0 9 S 1 4 0 13 . 5 1 :l . J
06/20/S3 20:00 9 .0 9 . {j Q.5 1 3 Q 11 . 5 13.0
06nO/83 2q: 00 B. 5 8 . :i ? 0 1 0 .0 B. 0 12. 5
00/21/83 04 00 B.O 7. j B. j 5.5 3. 5 9. 0
06121/83 08: 00 7 !i 7 5 7 c O. 0 3.~ 9 0 .oJ
06121/B3 1 ": . 00 7 j 7.5 8 Q 1 Z j 9.S 14 . ;;