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NOAA Technical Report ERL 415 - PMEL 34 Sources, Composition, and Transport of Suspended Particulate Matter in Lower Cook Inlet and Northwestern Shelikof Strait, Alaska Richard A. Feely and Gary J. Massoth Pacific Marine Environ mental Laboratory Seattle, Washington January 1982 u.s. Department of Commerce Malcolm Baldrige, Secretary National Oceanic and Atmospheric Administration John V. Byrne, Administrator Environmental Research Laboratories Boulder. Colorado George H. LUdwig, Director

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Page 1: Sources, composition, and transport of suspended ... · Sources, Composition, and Transport of Suspended Particulate Matter in Lower Cook Inlet and Northwestern Shelikof Strait, Alaska*

NOAA Technical Report ERL 415 - PMEL 34

Sources, Composition, and Transportof Suspended Particulate Matterin Lower Cook Inletand Northwestern Shelikof Strait, Alaska

Richard A. Feely and Gary J. Massoth

Pacific Marine Environ mental LaboratorySeattle, Washington

January 1982

u.s. Department of CommerceMalcolm Baldrige, Secretary

National Oceanic and Atmospheric AdministrationJohn V. Byrne, Administrator

Environmental Research LaboratoriesBoulder. ColoradoGeorge H. LUdwig, Director

Page 2: Sources, composition, and transport of suspended ... · Sources, Composition, and Transport of Suspended Particulate Matter in Lower Cook Inlet and Northwestern Shelikof Strait, Alaska*

NOTICE

Mention of a commercial company or product does not constitutean endorsement by NOAA Environmental Research Laboratories.Use for publicity or advertising purposes of information fromthis publication concerning proprietary products or the testsof such products is not authorized.

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CONTENTS

Page

ABSTRACT ....................................................................................................................... 1

1. INTRODUCTION. . . . . . . . . . . . . . . . . • . . . . . . . • . . . . . . . . . . . . . . . . . . . . . • . . . . . 1

2 . BACKGROUND .....•.•............................................. " 2

3. THE STUDY REGION 2

4. EXPERIMENTAL PROCEDURES .................................•.......• 5

4.1 Sampling Methods 54.2 Analytical Methods 8

5. RESULTS AND INTERPRETATION 9

5.1 Temporal Variability of Suspended Matter 175.2 Major Element Composition of the Suspended Matter 21

6. DISCUSSION .......•..••.............•..............•.•......•... " 24

7 . ACKNOWLEDGMENTS ..•................................••........... " 26

8. REFERENCES .........................•.....••.....••........•.... " 26

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Page 5: Sources, composition, and transport of suspended ... · Sources, Composition, and Transport of Suspended Particulate Matter in Lower Cook Inlet and Northwestern Shelikof Strait, Alaska*

Sources, Composition, and Transportof Suspended Particulate Matter in Lower Cook Inlet

and Northwestern Shelikof Strait, Alaska*Richard A. Feely and Gary J. Massoth

ABSTRACT. The chemical composition and seasonal distribution ofsuspended particulate matter collected during 1977 and 1978 inlower Cook Inlet and northwestern Shelikof Strait are comparedwith published data on current patterns. With respect to sus­pended-matter dispersal patterns, Cook Inlet shows characteristicsof both an estuary and an embayment. Estuarine characteristicsare exemplified by the association of the inorganic terrestrialmaterial from upper Cook Inlet with the outward-flowing estuarinewater. Plots of total suspended-matter concentrations versussalinity for surface and near-bottom waters are roughly linear forthe central region of lower Cook Inlet, indicating that dilutionof the estuarine water by relatively nonturbid oceanic water isthe major factor controlling suspended-matter concentrations inthe inlet. Embayment characteristics are indicated by thecross-channel suspended-matter gradients and by the elementalratios of the particulate matter, which show evidence for movementof Copper River-derived aluminosilicate material across the mouthof the inlet and into Shelikof Strait. These features, which areunique to lower Cook Inlet, are a direct result of the unusualnature of the current patterns existing within the inlet.

1. INTRODUCTION

The rapid expansion of petroleum and related industries in Cook Inlethas aroused considerable concern for the welfare of the local marine en­vironment and its renewable resources, especially the rich fisheries. Withfew exceptions, the region has not been subjected to massive oil spills, andthe effects of chronic, low-level inputs of petroleum products are onlybeginning to be addressed (Cline et al., 1979). Although various optionsfor allocation and transportation of Alaskan crude oil to west coast portsare still under consideration, it is clear that increasing amounts ofpetroleum will be transported through the region to meet the demand.

Since crude oil is only slightly water-soluble, it tends to form anemulsion when introduced into seawater, especially under intense waveaction. The emulsion has a high affinity for mineral particles and isadsorbed rapidly. Recent studies of oil spills in cQastal waters containingheavy loads of suspended matter have indicated rapid removal of oil by sorp­tion onto particles along the leading edge of frontal zones (Forrester,1971; Kolpack, 1971; Klemas and Polis, 1977). These zones are regions whereturbid estuarine water contacts seawater. At the interfaces downwellingusually occurs, causing the inorganic material and any associated con­taminants to be carried down into the seawater column. Similarly, labora­tory studies involving the interaction between crude oils and mineral

* Contribution No. 424 from the Pacific Marine Environmental Laboratory, NOAA

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particles show that significant amounts of oil may be accommodated by theparticles (Huang and Elliott, 1977; Feely et al., 1978). The accommodationprocess is a function of the isoelectric points of oil and mineral par­ticles, particle size and composition, temperature, and the ambient concen­trations of oil and mineral particles. Thus, the association of oil andsuspended particles can play an important role in the dispersal and deposi­tion of petroleum hydrocarbons, especially in an area like Cook Inlet, whichhas exceptionally high concentrations of suspended materials. This studycharacterizes spatial variations of the distribution and composition of sus­pended particulate matter in lower Cook Inlet and northwestern ShelikofStrait in order to identify likely dispersal routes of suspended matter andany associated petroleum hydrocarbons.

2. BACKGROUND

Previous studies of suspended material in lower Cook Inlet have beenlimi ted to observations of LANDSAT satellite and aircraft photographs,augmented with sea-truth measurements in some places. These studies haveprovided useful information about dispersal patterns of near-surfacesuspended matter, particularly in the Kalgin Island region where extremelyhigh concentration gradients have been observed. Sharma et al. (1974) usedthese sources of data to study suspended-matter distributions in Cook Inletduring late summer of 1972 and early spring of 1973. Concentrations ofsuspended matter ranged from 100 mgjL near the Forelands to 1-2 mgjL nearthe entrance of the inlet. Large temporal variations were related to tidalvariations in water circulation.

Gatto (1976) studied the dispersal of sediment plumes from coastalrivers as affected by tidal currents in the inlet. Turbid plumes from theTuxedni, Drift, Big, and McArthur rivers (fig. 1) on the west side formeddistinct surface layers, riding over and mixing with the saline water fromthe south. During flood tide, the plumes flowed northward along the coast.On ebb tide, the plumes migrated back to the south and west. Occasionally,the relict plumes were observed far offshore, which indicated that at leastsome plumes of sediment-laden water were capable of maintaining theiridentity for several tidal cycles.

Burbank (1977) used LANDSAT imagery to study dispersal patterns ofsuspended matter in Kachemak Bay, where the suspended material is derivedfrom inflow of inorganic and biogenic materials together with the salineGulf of Alaska water, in situ production, and suspended material dischargedfrom the Fox River and other local rivers. Sediment plumes were observedalong the northwest shore of inner Kachemak Bay. These plumes were divertedaround Homer Spit and into outer Kachemak Bay by a counterclockwise rotatinggyre. In the outer bay, the plumes moved to the west and north under theinfluence of a second counterclockwise gyre.

3. THE STUDY REGION

Physiographically, Cook Inlet is divided into three sections: the headregion, which is further divided into Knik and Turnagain arms; upper CookInlet; and lower Cook Inlet (fig. 1). Upper Cook Inlet is separated from

2

l

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,",

\\,,

II

//

2pO

\\ I /

GU~F 'Qr ALASKAI

/

'/

II

I

/

....----- Slevenson En/ranee

Elizab~th Ia c ""Cnugach I

Ji:p fJ..- Kennedy En/raneeBarren I

100

ALASKA

PENINSULA

156 0 1540 152 0 1500

Knik Arm

~harageFire 1.0

Turnagain

61 0 0 20 40 60 Nautical Miles

""""~61 0

I I I I

0 50 100 K IlomelersI I I

_:~ tN

IArea of Study

60 0 60 0

--- - _./ /- /

DEPTH I N METERS

56 0L.......L_

4_··.__-'----- L.L'/_-----'-"---1'-------'----_-----'- ----'--- ....l- .l..- L....I 5 6 0

Figure 1.--Physiographic setting of Cook Inlet and ShelikofStrait, Alaska.

-

3

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6000

0z0uw(/)

5000a::wCl..

(/)a::wI- 4000w::::!:

uiii::>u

~3000

u.i~

a::<t:l:U

2000(/)

0a::

tw~a::0 1000wz

+CD

-1-~ + -+-0 +u +

0J 0

Figure 2. --Combined monthly means and ranges for gaged major riversdischarging into Cook Inlet. The data were compiled from USGS stream­flow records for the following rivers and periods: Susitna River atSusitna, 1975-1978, mean annual discharge 1318 m3 /s; Knik River nearPalmer, 1961-1978, mean annual discharge 185 m3/s; Kenai River atSoldotna, 1965-1978, mean annual discharge 158 m3/s; and Matanuska Riverat Palmer, 1961-1973, mean annual discharge 104 m3/s.

lower Cook Inlet by two geographic constrictions: the East and the WestForelands. Below the Forelands, the coastline of lower Cook Inlet ischaracterized by several small embayments--Tuxedni Bay, Chinitna Bay, andIliamna Bay, and two large embayments--Kamishak Bay and Kachemak Bay. Atits mouth, the inlet opens into the Gulf of Alaska to the southeast, andShelikof Strait to the southwest. Shelikof Strait is separated from theGulf of Alaska by Shuyak, Afognak, Kodiak, and Trinity islands.

Upper Cook Inlet receives freshwater and suspended sediment from theMatanuska and Knik rivers at the head of Knik Arm and the Susitna and Belugarivers to the northwest. The combined flow of these rivers supplies about70% to 80% of the freshwater input and 75% to 90% of the suspended-sedimentinput to upper Cook Inlet (Rosenberg and Hood, 1967; Feulner et al., 1971).The rivers originate in glaciers and show large seasonal fluctuations indischarge (fig. 2). Peak discharge occurs in July and minimum discharge inMarch. Suspended sediment in these rivers is derived from glacial erosionat higher altitudes. In addition to the rivers discharging into upper CookInlet, the lower inlet receives suspended sediment from several smallerrivers that carry glacial flour into the inlet from both sides. Included inthis category are the Kenai, Kasilof, Ninilchik, Anchor, and Fox rivers onthe east side and the McArthur, Big, Drift, and Tuxedni rivers whichdischarge into the inlet from the west.

4

I..

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The physical oceanography of lower Cook Inlet has been described byseveral authors (Kinney et al., 1970; Wright et al., 1973; Gatto, 1976;Burbank, 1977; and Muench et al., 1978). The last reference provides themost complete description of water circulation. Water mass movement in theinlet is characterized by a net inward movement of oceanic water up theeastern shore and a net outward movement of a mixture of oceanic water andestuarine water along the western shore. In the vicinity of the Forelands,the water masses are vertically mixed because of the turbulent action oftidal currents. However, lateral separation of the water masses is apparentand results in a shear zone between the incoming saline water on the eastside and the outflowing estuarine water on the west. Coastal upwellingoccurs along the eastern shore from the region west of Kennedy Entrance toCape Starichkof.

The distribution and composition of bottom sediments in lower CookInlet have been studied (Sharma and Burrell, 1970; Bouma and Hampton, 1976;Hein et al., 1979). The sediments are composed primarily of medium- tofine-grained sands; however, occasionally silt- and clay-sized sedimentshave been observed. The deposits in the northern part of the inlet arewinnowed Pleistocene--early Holocene--gravels, and many of the particlessand-sized and smaller have been removed and redeposited to the south. Inaddition to relict sands and gravels, bottom deposits also contain somemodern fine-grained silts and clays. Hein et al. (1979) show that the claymineral suites in lower Cook Inlet are from two distinct sources. Achlorite-rich suite dominates the clay mineral fraction in deposits fromKennedy Entrance to Kachemak Bay. The Copper River appears to be the majorsource of this material as it discharges chlorite-rich, fine-grainedsediments into the northeast Gulf of Alaska which are then diverted to thewest and southwest by the coastal along-shelf currents (Hein et al., 1979;Feely et al., 1979). Apparently, some of this material reaches KennedyEntrance and is transported into lower Cook Inlet along with inflowing Gulfof Alaska water. The region to the west and north of Kachemak Bay isdominated by an illite-rich suite which has the Susitna-Knik-Matanuska Riversystem in upper Cook Inlet as its major source. Hein et al. (1979) suggestthat the distribution of clay minerals in bottom sediments of lower CookInlet reflects the dispersal routes of suspended matter in the overlyingwater. Thus, fine-grained particles from these two sources appear to followthe general pattern of water circulation in the inlet and also form the bulkof the mud deposits in the quiescent embayments along the shore.

4. EXPERIMENTAL PROCEDURES

4.1 Sampling Methods

In order to obtain information about seasonal variations of the dis­tribution and composition of suspended matter, samples were collected duringfive cruises in lower Cook Inlet. (4-16 April 1977, 28 June-12 July 1977,5-12 October 1977, 4-17 May 1978, and 22 August-6 September 1978). Figure 3shows the locations of the 1977 sampling stations, and figure 4 shows thelocations of the 1978 sampling stations. Water samples were collected inGeneral Oceanics Model 1070 10-L PVC Top Drop Niskin bottles from thesurface and 5 m above bottom at all stations, and from several intermediatedepths along vertical sections between Kachemak Bay and Kamishak Bay

5

-

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156° 154° 152° 150°

61° 61°

0 20 40 60 Nautical MilesI I I

0 50 100 KilometersI I !

_:~ tN

jArea of Study

60° 60°

57°

• !l1

!l8 a~.,':::'TR;'N'ITY•9 ISLANDS, .!>

56 0 :t\ 56°1560 1540 1520 1500

Figure 3.--Locations of 1977 sampling stations in lower Cook Inlet andShelikof Strait. During October, only stations 24-29 were occupied.

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• 4 MAY- 17 MAY 1978

afaf?ISLANDS

'p C8-7'" _8-822 AUG.- 6 SEPT. 1978 \, C8-6 ~ .C8-7

i C8-4 .. __~. . t(;)C8-3 W "'C8-5~~ ,:~

KAMISHAK C8-20. ,. :.,

~AC8-/.

.... 0 lla

", :'~'~p~,~, ~ r. --:~~~~~~EDOUGLAS 55-~ 5. /3

55-/1. STEVENSON

ENTRANCE

,

0 20 40 60 Nautical MilesI I I !

0 ~O 100 Kilometers! ! !

.~ tN. . j-. .

60° Area af Study

56° ~ 56°L...L. ---l. --L ....l.. ---'- ....l- ...l..- .J..J

150°

Figure 4.--Locations of 1978 sampling stations in lower Cook Inlet andShelikof Strait.

7

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(stations 25 through 29 on the 1977 cruises and stations CB1 through CB8 onthe 1978 cruises) and in Shelikof Strait (stations SS2, SS3, SS6, SS8, SS9,SS10, and SS12 in the 1978 cruises). To avoid the loss of rapidly settlingparticles (Gardner, 1977) and the resultant bias in elemental compositoncaused by fractionation (Calvert and McCartney, 1979), aliquots from eachsample were withdrawn promptly (within 10 to 15 minutes of collection), andvacuum filtered through 47-mm diameter, 0.4-~m pore size Nuclepore filtersfor total suspended-matter loading determinations and through 25-mm di­ameter, O. 4-~m pore size Nuclepore filters for elemental analyses. Allsamples were rinsed with three 10-mL aliquots of deionized membrane-filteredwater, placed in individual polycarbonate petri dishes with lids slightlyajar for a 24-hour dessication period over sodium hydroxide, and then sealedand stored for subsequent laboratory analysis.

Temperature and salinity data were obtained with a Plessey Model 9040CTn system equipped with a Model 8400 data logger. This system samplestwice per second for simultaneous values of conductivity, temperature, anddepth. The data were averaged to provide 1-m temperature and salinityvalues from which crt was computed. The crt values are accurate to ±0.02.

4.2 Analytical Methods

Total suspended-matter concentrations were determined gravimetrically.Samples of total suspended matter, collected on Nuclepore filters, wereweighed on a Cahn Model 4700 Electrobalance before and after filtration.The weighing precision (2cr = ±0.011 mg) and volume reading error (±10 mL)yield a combined relative standard deviation in suspended-matter concen­tration of approximately 1%. However, investigations of sampling precision(relative standard deviations ranging from 5% to 17%) suggest that theactual variability in particulate matter concentrations of these waters ismuch greater than the above analytical precision.

The major inorganic elements (Mg, AI, Si, K, Ca, Ti, and Fe) in thesuspended matter were determined by X-ray secondary emission (fluorescence)spectrometry using a Kevex Model 0810A-5100 X-ray energy spectrometer andthe thin-film technique (Baker and Piper, 1976). The inherent broadbandradiation from a silver X-ray tube was used to obtain a series of char­acteristic emission lines from a single-element secondary target which moreefficiently excited the thin-film sample. A sequence of Fe and Se targetswas used to fluoresce the aforementioned elements to provide maximumsensitivity and linearity. Standards were prepared from suspensions offinely ground* USGS Standard Rocks (W-1, BCR-1, AGV-1, and GSP-1) collectedon Nuclepore membrane filters identical to those used for sampleacquisition. The relative standard deviations for 10 replicate analyses ofa largely inorganic sample of approximately mean mass were less than 2% formajor constituents. However, when sampling precision was considered, therelative standard deviations increased to as much as 10%.

*By volume, 90% of the rock particles were less than 15 ~m in diameter asdetermined by scanning electron microscopy.

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5. RESULTS AND INTERPRETATION

Figures 5 through 8 show the distributions of salinity, temperature,at' and total suspended matter at the surface and at 5 m above the bottomfor the April and July 1977 cruises in lower Cook Inlet and Shelikof Strait.As shown in figures 5 and 7, the surface particulate matter distributionsare characterized by unusually high horizontal gradients. On the easternside, particulate concentrations were relatively low, ranging from 0.5 mg/Lnear Elizabeth Island to about 5.0 mg/L just north of Cape Ninilchik. InJuly, the nonturbid water remained close to the eastern shore and extendedat least as far north as the East Forelands. On the western side, suspendedloads increased sharply from concentrations averaging about 5.0 mg/L in thevicinity of Kamishak Bay to concentrations greater than 100 mg/L north ofTuxedni Bay. The salinity and temperature data in figures 5 and 7 showsimilar horizontal distribution patterns, reflecting the predominance of theinflowing, relatively clear, saline Gulf of Alaska water on the eastern sideand the outflowing turbid, low-salinity water from upper Cook Inlet on thewestern side. The outflowing estuarine water is transported to thesouthwest past Augustine Island and Cape Douglas into Shelikof Strait.

The near-bottom suspended-matter distributions (figs. 6 and 8) are verysimilar to the surface distributions, which suggests that cross-channelgradients in suspended-matter concentrations exist throughout the watercolumn. In agreement with this, vertical cross sections of the distributionof suspended matter and water properties from Kamishak to Kachemak Bay(figs. 9 through 13) show large cross-channel variations, which can be usedto identify three distinct water masses. On the west side (stations 28 and29 for the 1977 data, and stations CB1 through CB3 for the 1978 data) thewater properties are characterized by low salinity (29.8% 0 -31.6% 0 ) andhigh suspended-matter concentrations (0.9-8.2 mg/L). The water is virtuallyunstratified. These properties are characteristic of the outward-flowingestuarine water that originates in upper Cook Inlet and flows south alongthe western coast. This water mass contains much of the terrigenoussediment from the major rivers draining into upper Cook Inlet and lower CookInlet along the western shore. The central lower Cook Inlet region (sta­tions 25 and 26 for the 1977 data, and stations CBS and CB6 for the 1978data) contains water that is more saline (31.4% 0 -31.8% 0 ) and less turbid(0.4-1.4 mg/L) than the estuarine water to the west. This water is charac­teristic of inflowing Gulf of Alaska water which flows north along the eastside of the inlet. In Kachemak Bay (station 24 from the 1977 data andstations CB7 and CB8 from the 1978 data), the waters are relatively warmer,less saline (27.3% 0 -31.4% 0 ), and more turbid (0.9-2.8 mg/L) than thewater in the central region of the inlet. These waters generally displaythe most intense stratification, with maximum ~a values occurring duringthe July and August-September sampling periods. t

The May and August-September 1978 data show some patterns that areconsistent with data from the previous year. First, the outward-flowingestuarine water on the western side is colder in May and warmer in Aug­ust-September than the inward-flowing Gulf of Alaska water. This feature isconsistent with data obtained in April and June-July 1977 (figs. 5 and 7)and appears to be regulated by heat exchange between upper basin water andthe overlying continental air masses that exhibit relatively large seasonalfluctuations in temperature. Additionally, this feature is augmented by the

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Salinity (%0)Contour interval 0.5

Temperature (OC)

Contour inlerval 1,0

!rI

570

5S 0

600

590

15401560154"156"61"

l,,,-,-_11_"_--'-__----'__----:'-__.L-__-'--__-'-__-'" 56"

1560 1540 152" 1500152"154"156"

, ,56" .. II· 56"

61"Total Suspended

Sigma - t Matter (mg/ L)Contour interva I 0.5

~)5005.0-50,0

1.0-5.060"60" (1.0

59" 59"

---.... ITltflNIQ/If'1trllAItCI

,5S" 5S"

Figure 5.--Distributions ofpended matter at the surface

salinity, temperature,(4-16 April 1977).

and total sus-

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Salinity (%0)

Contour interval 0.5

Temperature (OC)Contour interval 1.0

58·

60°

59°

154°156·154·156·61·

60·

59·

I I

56· .. ~. 56·

61· 61·

Sigma-t Total Suspended

Contour interva IMatter (mg/ L)

~)5005.0-50.0

60· 1.0-5.0 60·<1.0

I

56· ......- ..-~1::5::6::.--.L---1~5~4:-::.--.L---1....l5-2-.-----'----...:j150.I

......_·_.. _--:' '--__......__......__......__--''--__''''56·156· 154· 152· 150"

Figure 6.--Distributions of salinity, temperature, at'suspended matter 5 m above the bottom (4-16 April 1977).

and total

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,56°t.L......:..:....----I.__.........__-'--_----''--_----'-__...L.-_----'l

Salinity (%0)

Contour interval 0.5

I•

J58°

57°

59°

60·

15201540156°

Temperature (OC)Contour interval 1.0

11.0"'-:-

, ".--:-.. 10.0.....__---'__---''--__.......,,----_.L...__......__......__...., 56°

154°156°61°

61°Sigma - tContour interva I 0.5

L

61°

58°

57°

59°

152°1540156°

Total SuspendedMatter (mg/L)

~)50'0

5.0-50.01.0-5.0<1.0

152°~54°156°

60°

58°

Figure 7. --Distributions ofpended matter at the surface

salinity, temperature, at'(28 June-12 July 1977).

and total sus-

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57'

58'

59·

so·

154015S·

Temperature (OC)Contour interval 1.0

154·15S·

Salinity (%0)

Contour interval 0,5

6/·

I I

5S· ¥- ~\ 56'15S· 154· 152· 150· 15S' 154' 152" 150'

Figure 8.--Distributions of salinity, temperature, at' and total sus-

pended matter 5 m above the bottom (28 June-12 July 1977)

59· 59·

--- srcVCIt$()Ii(eNTRANce

0

58· 58·

I I

56" ~\ ~,

56"

SI"

Sigma-t Tota I SuspendedContour interval 0.5 Malter (mg/Ll

~>5005.0-50.0

SO· 1,0-5,0 so·<1.0

13

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150I

2'

50I

2'

FROM WESTERN SHORE OF KAMISHAK BAY,IN KILOMETERS

150 0I "o.,g'w ,,4·',Z'W

2.

100

STATIONS27 26 2~

DISTANCE

~I

282.

VI 40II:...I-...

60 60~

~

£ 80 80

l-ll.... 1000 100

120 120~

Salinity (%.) Temperature (·Cl~

140 Contour interval 0.2 140 Contour interval 0.5

DISTANCE FROM WESTERN SHORE OF KAMISHAK BAY,

IN KILOMETERS

0 50 100 150 0 50 100 150I I

STATIONSI

1,4·'12'WI

STATIONSI

,,4-'2'W "0·'9'. 150·5,'.2. 28 27 2. 25 24 2. 28 27 2. 25 24

VIII:...I­...~

Z

:J:l­ll....o 100 100

120

Sigmo-t

140 Contour interval 0.1

120 Total Suspended

Moller (mg/L)

140 Contour interval 1.0

Figure 9. --Vertical cross sections of the distributions of salinity,temperature, at' and total suspended matter for stations 24-29 in lower

Cook Inlet (4-16 April 1977).

relatively longer period of advective replacement of water in upper CookInlet (Muench et al., 1978). Second, suspended-matter concentrations in theKamishak Bay region are higher in early spring than in late summer eventhough there is more freshwater input into lower Cook Inlet during latesummer (fig. 2). A possible explanation for this phenomenon is that inearly spring, when most of the ice breakup occurs in upper Cook Inlet, re­suspension and transport of previously deposited sediments may result fromthe ice movement. Another possibility is that in spring, turbulent mixingis sufficiently intense throughout the inlet to cause resuspended sedimentto be mixed vertically throughout the water column and, in particular, inthe Kamishak Bay region. Although the temperature, salinity, at' and total

suspended-matter data in figures 9 and 12 support the second possibility,

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DISTANCE FROM WESTERN SHORE OF KAMISHAK BAY,

IN KILOMETERS

C/la: 40

""I-""::. 60Z

I 80I­0.

""o 100

120

~OI

28

100

STATIONS27 26

I~OI

t!50"~9'W

100

120

140Salinity (%0)

Contour InlerIJol 0.2 140Temperature (OC)

Contour inter'v'ol 0.5

DISTANCE FROM WESTERN SHORE OF KAMISHAK BAY,IN KILOMETERS

C/la:""I-"" 60::.Z

80II-0.

"" 100o

29

50I

2.

100

STATIONS27 26

40

60

80

100

50I

28

100I

STATIONS27 26

150I

120

SIQmo-t

140 Conlour interval 0.5

120 Total Suspended

Matter (mQ/ L)

140 Contour interval 0.5

.-.~.

Figure 10. --Vertical cross sections of the distributions of salinity,temperature, at' and total suspended matter for stations 24-29 in lower

Cook Inlet (23 June-12 July 1977).

the first explanation cannot be rejected entirely because higher concentra­tions of surface suspended matter are observed throughout the inlet in earlyspring relative to early summer (figs. 5 through 8). Indeed, both processesmay be contributing to this effect.

Figure 14 shows vertical cross sections of temperature, salinity, at'

and total suspended matter for stations located in Shelikof Strait. Thedata were obtained on the August-September 1978 cruise. Stations SS2, SS3,SS6, SS8, SS9, SS10, and SS12 represent a longitudinal cross section alongthe main axis of the strait. Stations SS4 through SS7 and SSll through SS13represent transverse cross sections at midstrait and upperstrait, respec­tively. Cross-channel gradients of temperature, salinity, and suspended

15

-

Page 20: Sources, composition, and transport of suspended ... · Sources, Composition, and Transport of Suspended Particulate Matter in Lower Cook Inlet and Northwestern Shelikof Strait, Alaska*

VIa:

'"....~ 60

~

:I: 80....<l.

~ 100

120

29

~OI

DISTANCE FROM WESTERN SHORE OF KAMISHAK BAY,IN KilOMETERS

I ~o 0 ~oI I I

I!!lO·!!l9'W I !!l4·12'W2t 28

100

120

I~OI

Salinily (O/ool140 Contour interval 0.2

Temperature (OCl140 Contour interval 0.2

DISTANCE FROM WESTERN SHORE OF KAMISHAK BAY,

IN KilOMETERS

100 150I I

STATIONS 100·"·W27 26 2!l 24

50I

28

100

120 Total Suspended

Matter (moll)

140 Contour I nter va I 0.5

100I

STATIONS27' 26

50I

2829

VI 40a:

'"....'" 60::EZ

~ 80

....<l.

'" 1000

120

Siomo-t140 Contour interval 0.2

Figure 11. --Vertical cross sections of the distributions of salinity,temperature, at' and total suspended matter for stations 24-29 in lower

Cook Inlet (3-12 October 1977).

matter are consistent with cross-channel gradients observed in lower CookInlet. In particular, the surface temperature, salinity, and suspended­matter values at SSll in Shelikof Strait are nearly the same as correspond­ing parameters at CB3 and CB4 in lower Cook Inlet for the same samplingperiod (fig. 13). This evidence strongly supports the view that water andsuspended material from western lower Cook Inlet are transported intoShelikof Strait. There is also evidence for a near-bottom nepheloid layer inthe strait, in the lower 50-60 m of the water column. Since there are nocorresponding large gradients in at that would tend to buoy up suspended

material, the bottom nepheloid layer in this region is probably a result ofresuspension of bottom sediment.

L

16

Page 21: Sources, composition, and transport of suspended ... · Sources, Composition, and Transport of Suspended Particulate Matter in Lower Cook Inlet and Northwestern Shelikof Strait, Alaska*

DISTANCE FROM WESTERN SHORE OF KAMISHAK BAY,IN KILOMETERS

150I

100I

STATIONS4 ~

50I

C8·1

100I

STATIONS. ~

~uI

CB·I

III 40 40a:~ :;:. ,~

:;..~ 60 60 ::~ .2

~~;.. .;~..! 151-

l~, •

:.. ~~.

:. 80 .:" 80 .:',"j- ~ ... ~ ..

A.~ '., ~~.: .Q 100 L 100

~~:..';'~..

~('...120 -;.", 120 .:.

;~..Temperature (OC) t:

140 140 Contour interval 02.....

150I

100I

STATIONS4 ~

50I

CB·I

Total SuspendedMatter (mg/L)Contour interva I 0.5

80

100

140

120

0, •

"i-\-.:/{',1'; •.

DISTANCE FROM WESTERN SHORE OF KAMISHAK BAY.IN KILOMETERS

150 0I I

ISO·S9'W IS4"12'W

100I

STATIONS. ~

~OI

CS-I 2

Si(,lma- tContour interval 0,2

120

140

III 40a:~

~

~ 60

!:. 80~A.

~ roo

Figure 12. --Vertical cross sections of the distributions of salinity,temperature, at' and total suspended matter for stations CB-1 through

CB-8 in lower Cook Inlet (4-17 May 1978).

5.1 Temporal Variability of Suspended Matter

In order to obtain information about short-term variations of sus­pended-matter concentrations in the inlet, time-series experiments wereconducted at station CB7 in Kachemak Bay and stations CB9 and CB10 oneither side of Kalgin Island. Water samples from the surface and 5 mabove the bottom were collected and filtered every two hours. The re­sul ts of these experiments are shown in figure 15. High and low tidesare represented in the figures by arrows. Reference points for thetidal data are in the caption. On either side of Kalgin Island,suspended-matter concentrations are highly variable both at the surface

17

Page 22: Sources, composition, and transport of suspended ... · Sources, Composition, and Transport of Suspended Particulate Matter in Lower Cook Inlet and Northwestern Shelikof Strait, Alaska*

DISTANCE FROM WESTERN SHORE OF KAMISHAK BAY,IN KILOMETERS

150I

100I

STATIONS4 ,

50I

ce·1

oI

154"12' w

60

"",

80•... ,:~

100

120

Temperature (OC)140 Contour interval 0,5

150I

100I

STATIONS4 ,

o1

154·12'W

(J) 400::UJI-UJ 60::l;

z

£ 80I-Cl.UJa 100

120

Sal inlt y (%0)140 Contour interval 0,5

DISTANCE FROM WESTERN SHORE OF KAMISHAK BAY,IN KILOMETERS

Sillmo -tContour interval 0,5

150I

,,~.

, :."

. '\

100I

STATIONS4 5

50I

CB·I

Toto I SuspendedMatter (mIl/L)Contour Interval 0,5

eo

120

100

140L....::::.::.:.:.:::::.....:.:.:.:.:.:..:..:.:....:.:.:..-----=--'

150I

•100

STATIONS4 5

50I

C8·1

o1

1~4·I2'W

140

120

(J)0::UJI-UJ2z

-£ eoI-C1.UJ

1000

Figure 13. --Vertical cross sections of the distributions of salinity,temperature, at' and total suspended matter for stations CB-1 through

CB-8 in lower Cook Inlet (22 August-6 September 1978).

(10-180 mg/L) and near the bottom (28-254 mg/L). Highest concentrationswere obtained at station CB10 on the east side of Kalgin Island. Surfacemaxima occurred shortly before low tide and exhibited a diurnal char­acter. Tidal currents converge here, current velocities are high, andthe water column is vertically mixed, causing complex circulation pat­terns (Gatto, 1976). On the west side of the island, flow patterns weredominated by tidal currents, with maximum suspended-matter concentra­tions in surface waters usually occurring during flood tide. This wasprobably the result of lateral movement of relict suspended-matterplumes from the coastal rivers along the western shore (Gatto, 1976).

l

18

Page 23: Sources, composition, and transport of suspended ... · Sources, Composition, and Transport of Suspended Particulate Matter in Lower Cook Inlet and Northwestern Shelikof Strait, Alaska*

E.."

o '0'---------'KI!..0 .. (1[R5

HE"'0

Salinity (%olContour In'.rvol 05

o .0"----------'

KILOMETERS

swn·r

100

200

E.."

o '0'---------'Il:I1.OMf.T£AS

W'5-11

SE7

o . ":.:'. to'---------'

11.I!..0 .. £,£R5

HE"

Temperature (OelContour 'n,.rvol 0.5

o .0"----------'KILOMETERS

10

: : .~. : . ;;:jSW

55-2

100

200

o '0'---------',(ll.o .. niItS

o '0'---------'IW•. OM[HltS

w E5S-11 II ~o I'

.o~Coo~------:. . f

07'. . \.

~o '07. d.~O"5.J~(.'" . :

, SE• 7

~oKII..O .. [T[R5

~oIUI..O ..[,[R5

HE

"

,HE

10 II

10

Sigma -IContour Inllr'lol 0.5

o .0"----------'

KlLOM[ T[RS

Total SuspendedMatter Img/LIContour Inl.nal 0,25

o .0~

KILOMETERS

r!---!----'----!----!----!--m"swII-t

sw11·1

200

100

200

100

300

sections of the distributionssuspended matter for stations

of salinity,SS-2, SS-3,

Strait (22 Aug-ShelikofinSS-13andSS-12,

crosstotalandat'

SS-8, SS-9, SS-lO,September 1978) ..

Figure 14. --Verticaltemperature,

SS-6,ust-6

19

Page 24: Sources, composition, and transport of suspended ... · Sources, Composition, and Transport of Suspended Particulate Matter in Lower Cook Inlet and Northwestern Shelikof Strait, Alaska*

TIME (LOCAL)

o 0 0o 0 0

8 ~ ~9-2

*1\1\I \ /I \ I

"trtrA.., I ir'\ J~ 't._~

9-1T I ME (LOCAL)

/I

"IIIIII,,II

~ I\ ,~4

10 0 0 10

'8 ~ ~ '0o 0 0 ~8-31

oo<D

48-HOUR TIME SERIESCRUISE RP4-DI-7BB-1!CB-IO, 31 AUGUST- 2 SEPTEMBER, 197BBottam Samples (~Om)

8N

40

20

oo~

5-14

btHigh tide 220l Low tide

200-6- Surface

..... Bottom IBO

160

140

120

100

BO

o5-13

50-HOUR TIME SERIESCRUISE RP4-DI-78A-111

CB-9, 12-14 MAY, 1978

Bottom Samples (~31 m)

~ l ~ g ~N 0 0

5-12

a

120

100

140

a:w~

..J

a:Wa.<J)

~<la:Cl

..J

..J

C4.0;;...----------------':""1

owozwa.<J):::)<J)

..J<l~

o~

52-HOUR TIME SERIESCRUI SE RP4-DI-7BA-11ICB-7, 7-9 MAY, 1978Bottom Sample. (-49m)

3,0

4\\

10

0 0 0 l8 0 0 19 0 0 f5 00 0 0 0

~0 00 N N <D N N

~ ! ~ N 0 0 ~ ~ N 0

5-7 5-8 5-9TIME (LOCAL)

Figure 15.--Temporal variability oftotal suspended matter at the surfaceand 5 m above the bottom at threetime-series stations in lower CookInlet. Reference points for tidaldata are (A) Drift River TerminalTide Station, (B) Kenai City Pier,and (C) Homer.

Near-bottom particulate maxima did not show a consistent periodic­ity, but peaks associated with both ebb and flood currents were evident.Furthermore, near-bottom suspended-matter concentrations were generallyhigher than at the surface. These data indicate that when the near­bottom tidal currents reached maximum velocity, resuspension of bottomsediment increased significantly.

The surface data at the Kachemak Bay station (CB7) show greatlyreduced concentration fluctuations. With the exception of the last 16hours of data, all of the surface variability is within the samplingerror. Only one peak associated with ebb current exceeds the estimatedsampling precision by more than a factor of two. This may be caused bysouthward movement of sediment plumes from the Anchor and NinilchikRivers during ebb tide (Burbank, 1977). This result is consistent withthe general conclusion of Gatto (1976) based on observations of LANDSATimages of lower Cook Inlet, that turbid plumes were more prominent inthe southern and central part of the lower inlet just after ebb current.

l

20

Page 25: Sources, composition, and transport of suspended ... · Sources, Composition, and Transport of Suspended Particulate Matter in Lower Cook Inlet and Northwestern Shelikof Strait, Alaska*

5.2 Major Element Composition of the Suspended Matter

In order to further characterize the primary sources of suspendedmaterial in lower Cook Inlet, samples of particulate matter wereanalyzed for their major inorganic elements. The resulting data havebeen segregated into five regions: Kalgin Island and upper Cook Inlet,Kamishak Bay, Kachemak Bay, Kennedy and Stevenson entrances, and north­western Shelikof Strait. The averaged chemical data, along with thosefrom the combined Susitna-Knik-Matanuska River system and the CopperRiver, are given in table 1. The Cook Inlet data represent regional andseasonal composites; therefore, they exhibit rather large ranges ofvalues and standard deviations, primarily because of relative (in timeand space) biogenic dilution. The last two columns in table 1, biogenicsilicon percentages and estimated percentages of aluminosilicates, givea measure of this dilution for the various regions. The river data repre­sent a single-point-in-time sampling, that of maximum discharge. The CopperRiver data give an estimate of the precision of the analytical technique,whereas the combined upper Cook Inlet river data reflect the error ofaveraging values from several locations. In general, suspended materialfrom upper and western Cook Inlet has nearly the same elemental compositionas the river samples. This is especially true for the majorrock-forming elements (Ai, K, Ti, and Fe), which are almost exclusivelyassociated with aluminosilicate minerals of terrestrial origin (Price andCalvert, 1973; Feely et a1., 1981). The high concentrations of theseelements in the suspended matter from lower Cook Inlet indicate thataluminosilicate minerals are a predominant phase in the particulate matter,ranging from 49% in the Kachemak Bay samples to 98% in the samples fromKamishak Bay. The remaining material consists of organic matter andbiogenic tests.

To identify the sources of the aluminosilicate materials in suspension,several authors have examined interelement ratios (Spencer and Sachs, 1970;Price and Calvert, 1973; Feely, 1975; Baker and Feely, 1978; Feely et al.,1981). Table 2 uses the averaged chemical data in table 1 to generateratios of the major elements to aluminum. This procedure minimizes theeffects of dilution by terrestrial and marine biogenic matter. The datashow that aluminosilicate material from the Copper River has higher Mg/Al,Ca/Al, and Fe/Al ratios and a lower K/Al ratio than suspended matter fromthe Susitna-Knik-Matanuska River system. This is as expected, sincechlorite minerals are characteristically enriched in Mg, Ca, and Fe anddepleted in K relative to illites (Deer et a1., 1962). Similarly, theelemental ratios of the particulate samples from the various regions inlower Cook Inlet are indicative of the sources for these materials. Theelemental ratios of samples from Kennedy Entrance and Kachemak Bay aresimilar to elemental ratios for Copper River suspended matter, whereassamples from the Kalgin Island and Kamishak Bay regions more closely re­semble the elemental ratios of suspended matter from the upper Cook Inletrivers.

This similarity is best illustrated by comparing K/Ca ratios. The K/Caratio of Copper River suspended matter is 0.40, signifying the enrichment ofCa and depletion of K in a chlorite-rich mineral suite relative to an illite­dominated suite. In contrast, suspended material from the Susitna-Knik­Matanuska River system has a K/Ca ratio of 1.14. K/Ca ratios in the Kennedyand Stevenson entrances and Kachemak Bay samples are 0.48 and 0.47 respec­tively, indicating that the Copper River is the primary source for the

21

Page 26: Sources, composition, and transport of suspended ... · Sources, Composition, and Transport of Suspended Particulate Matter in Lower Cook Inlet and Northwestern Shelikof Strait, Alaska*

Tab

le1

.--A

ver

aged

1977

-197

8ch

emic

alco

mp

osi

tio

nd

ata

for

surf

ace

susp

end

ed­

matt

er

sam

ple

sfr

omse

lecte

dre

gio

ns

des

crib

edin

the

tex

t

Reg

ion

n

Su

sitn

a-K

nik

­M

atan

usk

aR

iver

syst

em13

Kal

gin

Isla

nd

­u

pp

erC

ook

Inle

t9

Mg

wt.

%i1

0

3.7

3iO

.61

3.0

5iO

.67

Al

wt.

%i1

0

10

.39

i2.0

3

8.5

9i1

.91

Si

wt.

%i1

0

33

.41

i3.4

2

28

.57

i6.0

5

K wt.

%i1

0

2.2

6iO

.63

1.9

5iO

.38

Ca

wt.

%i1

0

1.9

8iO

.58

1.7

3iO

.38

Ti

wt.

%i1

0

0.6

07

iO.0

59

0.5

05

iO.0

85

Fe

wt.

%i1

0

6.3

9iO

.40

5.3

3iO

.90

Bio

gen

icS

iw

t.%

0.0

0

0.9

4

Est

imat

edalu

min

osi

licate

wt.

%

104 86

N N

Kam

isha

kB

ay

Kac

hem

akB

ay

5 6

3.6

9iO

.59

2.1

5i1

.02

9.8

4i1

.66

4.8

5i2

.78

34

.82

i3.7

6

30

.38

i8.7

2

2.0

9iO

.36

0.8

1iO

.53

1.7

7iO

.25

1.7

4iO

.95

0.4

83

iO.0

84

0.2

87

iO.1

59

5.3

1iO

.79

2.9

5i1

.68

3.1

5

14

.75

98 49

Ken

ned

y-S

tev

enso

nen

tran

ces

91

.68

i1.1

13

.91

i2.5

52

7.8

2i5

.48

0.6

5iO

.48

1.3

6iO

.55

0.2

05

iO.1

26

2.0

3i1

.58

15

.24

39

NWS

heli

ko

fS

trait

Cop

per

Riv

er

6 5

2.9

8iO

.73

4.6

5iO

.17

7.0

2i2

.14

9.2

5iO

.19

33

.46

i4.0

1

27

.91

iO.5

4

1.3

2iO

.47

1.7

8iO

.03

1.7

1iO

.55

4.4

2iO

.09

0.3

53

iO.1

I8

0.6

38

iO.0

13

3.6

4i1

.32

6.7

0iO

.16

10

.87

0.0

0

70 93

NO

TE:

Ex

cess

(bio

gen

ic)

Si

%w

asd

eter

min

edre

lati

ve

toS

usi

tna-

Kn

ik-M

atan

usk

aR

iver

syst

emS

i/A

lv

alu

eo

f3

.22

.E

s­ti

mate

dalu

min

osi

licate

%v

alu

es

wer

eo

bta

ined

by

mu

ltip

licati

on

of

resp

ecti

ve

reg

ion

al

Al

%b

y10

(Sack

ett

and

Arr

hen

ius,

19

62

).

Page 27: Sources, composition, and transport of suspended ... · Sources, Composition, and Transport of Suspended Particulate Matter in Lower Cook Inlet and Northwestern Shelikof Strait, Alaska*

Tab

le2

.--E

lem

ent/

Al

and

K/C

ara

tio

sfo

rd

ata

pre

sen

ted

inT

able

1

Reg

ion

Mg/

AI

Si/

AI

K/A

IC

a/A

IT

i/A

IF

e/A

IK

/Ca

Su

sitn

a-M

atan

usk

a-K

nik

Riv

ersy

stem

0.3

59

3.2

20

.21

80

.19

10

.05

80

.61

51

.14

Kal

gin

Isla

nd

-N

up

per

Coo

kIn

let

0.3

55

3.3

30

.22

80

.20

10

.05

90

.62

11

.13

VJ

Kam

isha

kB

ay0

.37

53

.54

0.2

12

0.1

82

0.0

49

0.5

40

1.1

7

Kac

hem

akB

ay0

.44

36

.26

0.1

67

0.3

59

0.0

59

0.6

08

0.4

7

Ken

ned

y-S

tev

enso

nen

tran

ces

0.4

30

7.1

20

.16

60

.34

80

.05

20

.51

90

.48

NWS

hel

iko

fS

trait

0.4

24

4.7

70

.18

80

.24

40

.05

00

.51

90

.77

Cop

per

Riv

er0

.50

33

.01

0.1

92

0.4

78

0.0

69

0.7

24

0.4

0

Page 28: Sources, composition, and transport of suspended ... · Sources, Composition, and Transport of Suspended Particulate Matter in Lower Cook Inlet and Northwestern Shelikof Strait, Alaska*

aluminosilicate fraction of the suspended matter in these regions. Suspendedmaterial from Kalgin Island and Kamishak Bay have KjCa ratios of 1.13 and1.17, respectively. These data indicate that the Susitna-Knik-MatanuskaRiver system is the major source for the suspended matter in these regions.In northwestern Shelikof Strait, the KjCa ratio in the suspended matteris approximately 0.77. This ratio is indicative of an admixture of alumino­silicate material from both sources. This indication is supported by theMgI Al and CalAl ratios, which are also elevated in comparison with re­spective values for the combined Susitna-Knik-Matanuska River system. Thesefindings indicate that the aluminosilicate material in northwestern ShelikofStrait is largely a composite of illite-rich material discharged into upperCook Inlet from the Susitna-Knik-Matanuska River system and chlorite-richCopper River material.

6. DISCUSSION

In a discussion of circulation patterns in lower Cook Inlet, Muench etal. (1978) described the inlet as having characteristics of both an estuaryand an embayment. The estuarine characteristics are illustrated by the out­flowing low-salinity water from upper Cook Inlet which laterally entrainswater from the eastern side of the inlet, whereas cross-channel flow at themouth of the inlet is described as being more characteristic of flow in alarge embayment. The same kind of analogy can be used to describe thegeneral features of suspended-matter distributions and dispersal patterns inthe inlet. Estuarine characteristics are exemplified by the association ofthe inorganic, terrestrial material from upper Cook Inlet with the outward­flowing estuarine water. Figure 16 shows plots of total suspended-matterconcentrations versus salinity for surface and near-bottom waters from thecentral part of the lower inlet. The plots are roughly linear, indicatingthat dilution of the estuarine water by relatively nonturbid oceanic wateris the major factor controlling suspended-matter concentrations in the lowerinlet. Embayment characteristics are indicated by the cross-channelsuspended-matter gradients and by the evidence for movement of CopperRiver-derived aluminosilicate material across the mouth of the inlet andinto Shelikof Strait.

Figure 17 shows a generalized scheme of suspended-matter dispersal inlower Cook Inlet. It represents a composite of this study and suspended­matter studies by Gatto (1976) and Burbank (1977). The major features ofthe dispersal patterns are (1) bifurcation of the inflowing oceanic water,with a portion of the aluminosilicate material from the Copper River flowingup the eastern side of the inlet and with some entrainment by the outflowingestuarine water, and the remaining material flowing across the mouth of theinlet and down into Shelikof Strait; and (2) movement of the turbidestuarine water, enriched in aluminosilicate material from the Susitna andother rivers along the western shore, around Cape Douglas and into ShelikofStrait. These results provide further support for the general conclusion ofHein et al. (1979) that the major controlling force affecting suspended­sediment distributions is the strong, semidiurnal tidal currents augmentedby the estuarine and embayment types of circulation patterns present in theinlet.

The significance of these results is apparent when dispersal routes forenvironmental contaminants, particularly crude oils, are considered. As

24

Page 29: Sources, composition, and transport of suspended ... · Sources, Composition, and Transport of Suspended Particulate Matter in Lower Cook Inlet and Northwestern Shelikof Strait, Alaska*

26.0 27.0 28.0 29.0 30.0 31.0 32.0SALINITY, IN GRAMS PER KILOGRAM

Y=1318.9-41.IXr =-0.90

26.0 27.0 28.0 29.0 30.0 31.0 32.0

SALINITY, INGRAMS PER KILOGRAM

b50.0

150.0

100.0

200.

••

Y =1650.9 - 52.5Xr = -0.95

••

a

-a:: a::Ww 300.01-1-1--<{-..J

2500~a::

OWwU- 200.0o(/}z~w<{ 150.0u-a::(/}<.:):J- 100.0(/}-..J

-..J-..J-<{~ 50.0I- z0_I-

Figure 16.--Scatter plots of the relationships between total suspendedmatter and salinity for (A) surface and (B) 5 m above the bottom in thecentral region of lower Cook Inlet (4-16 April 1977).

stated earlier, experiments conducted in our laboratory have shown thatsuspended materials from lower Cook Inlet are capable of accomodating up to11% of their weight in Cook Inlet crude oil (Feely et al., 1978). Theparticles with adsorbed oil formed spherical aggregates that ranged indiameter from 5 to 45 IJm. Using Stoke's settling model, these authorsestimated that settling velocities for the aggregates ranged between 0.6 and30m/day. This suggests that in the absence of vertical turbulence anddissolution processes, it would take from ~2 to ~117 days for the aggregatesto fall through a water column of 70 00, the average depth near the mouth ofthe inlet. Thus, the aggregates of oil and suspended matter could be

Figure 17.--Generalized scheme ofsuspended-matter dispersal routesin lower Cook Inlet and northernShelikof Strait.

25

Page 30: Sources, composition, and transport of suspended ... · Sources, Composition, and Transport of Suspended Particulate Matter in Lower Cook Inlet and Northwestern Shelikof Strait, Alaska*

distributed throughout the inlet before they were (eventually) deposited inquiescent embayments along the shore or carried into Shelikof Strait.

7. ACKNOWLEDGMENTS

The authors express their appreciation to Captain Sidney Miller and thecrew of the Discoverer, without whose help this work would not have beenpossible; Mr. Albert Chapdelaine, Mr. Randy Dyer, Ms. Jane Hannuksela, Mr.William Landing, Mr. Anthony Paulson, and Ms. Joyce Quan for assisting insample collection; Ms. Marilyn Lamb for preparing the figures; and the U.S.Geological Survey Water Resources Division, Anchorage, for providing runoffdata. The authors also express their appreciation to James R. Hein and DavidE. Drake of the U. S. Geological Survey at Menlo Park for providing criticalreviews of this report. This study was supported in part by the Bureau ofLand Management through interagency agreement with the National Oceanic andAtmospheric Administration under which a multiyear program responding toneeds of petroleum development of the Alaskan continental shelf is managedby the Outer Continental Shelf Environmental Assessment Program (OCSEAP)Office.

8. REFERENCES

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28'i'; us GOVERNMENT PRINTING OFFICE 1982~576-00111223 Region No 8