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J. Duhok Univ. Vol.13, No.1, (Agri. And Vet. Sciences) Pp 82-89, 2010<br />

which is caused by rainfall, snowfall and<br />

runoff flow, will also increase the turbidity of<br />

water. Suspended materials include soil particles<br />

(clay, silt, and sand), algae, plankton, microbes,<br />

and other substances. <strong>The</strong>se materials are<br />

typically in the size range of 0.004 mm (silt) to<br />

1.0 mm (sand). Turbidity can affect the color of<br />

the water. A variety of methods to estimate<br />

seasonal suspended sediment yield in a mixed<br />

land-use catchments they have examined.<br />

Despite the inherent uncertainty, all estimates of<br />

catchments sediment yield are found to be high<br />

with respect to erosion plot studies from the<br />

local area, and this suggests the importance<br />

channel erosion as major sediment sources, a<br />

finding consistent with other regional studies<br />

.Usually, we measure turbidity to provide a<br />

cheap estimate of the total suspended solids or<br />

sediments (TSS) concentration (Kg dry soil<br />

weight /m 3 water).Turbidity is measured using<br />

the techniques of turbid meter or nephelometry<br />

and is expressed in arbitrary units<br />

(Nephelometric Turbidity Unit, NTU). <strong>The</strong><br />

direct relationship between turbidity data and<br />

suspended solids concentration depends on many<br />

factors, including particle size distribution,<br />

particle shape and surface condition, refractive<br />

index of scattering particles and of the<br />

suspension medium and wavelength of the light.<br />

Another even cheaper method is to use an<br />

inexpensive devise called "Turbidity Tube" is a<br />

simple adaptation for streams of the "Secchi<br />

disk" technique for lakes. It involves looking<br />

down a tube at a black and white disk and<br />

recording how much stream water is needed to<br />

make the disk disappear.<br />

MATERIAL AND METHOD<br />

Study locations<br />

Duhok river catchments consist of following<br />

secondary laterals , Bagloor, Sendor, Garmava<br />

and Khazava catchments , the total catchments<br />

area is 133.8 Km 2 the site between latitudes (36 o<br />

52 - - 37 o 01 - N) and Longitude (42 o 51 - - 43 o 06 -<br />

E) .<strong>The</strong> highest mountain peak at Bakhar (1381<br />

m) above sea and the lowest outlet point is 560m<br />

above sea, the attached morphometric map (Fig<br />

.1) showing the site with scale (1:110000)(<br />

Aomer , 1999) Garmava river length is<br />

(14.1Km) the catchments shape as triangle, it is<br />

far Duhok city about (5Km) . Duhok Dam<br />

watershed climate region varies continually<br />

between dry in summer and wet in winter ,the<br />

rain fed area in the watershed is highly to<br />

moderate slopes and cultivated with venues and<br />

grain ( Hammed,2004) . Physical soil analysis of<br />

Duhok watershed show that the most soil,<br />

contained highly clay material, which about<br />

more than 36% and it's classified as silt clay soil<br />

with normal to moderate acidity. Only 25% of<br />

Duhok watershed was covered with forest<br />

(Gulcur and Kettaneh, 1972) but now day is less<br />

than the mention percentage even though the<br />

governorate cultivated 2.6% of forested trees as<br />

well as 6.5km of wattle fences and constriction<br />

about (3250m 3 ) prevent check dam in gullies to<br />

reduce surface runoff then reduce water erosion<br />

in the region. <strong>The</strong> erosion is their active due to<br />

the sever slope and the rate of deposit<br />

sedimentation is high .<strong>The</strong> main purpose of this<br />

study is to estimated the seasonal sedimentation<br />

for the Duhok dam watershed through<br />

continually samples during the seasonal runoff<br />

which outlet to the Duhok river due to estimate<br />

their turbidity and to find the unique relationship<br />

between turbidity and suspension concentrations<br />

using turbidity meter (HACH-2100A).Turbidity<br />

can be measured in the laboratory and also onsite<br />

in the river by a handheld turbidity meter.<br />

<strong>The</strong> meter is calibrated using standard samples<br />

from the meter manufacturer. Six glass of vials<br />

shows turbidity standards of (0.6, 1, 10,100,<br />

500) and (1000 NTUs). Once the meter is<br />

calibrated to correctly read these standards, then<br />

turbidity of runoff suspended water samples can<br />

be taken.<br />

<strong>The</strong> methods and equipment used for<br />

sampling suspended sediment are different from<br />

those used for deposited sediments. Also<br />

sampling methods for measurements of the<br />

quantity of sediment in transport are different<br />

than for measurement of sediment quality. <strong>The</strong><br />

reason for these differences reflects the fact that<br />

sediment quantity must include the sand size<br />

fractions which are unequally distributed in<br />

depth, whereas sediment quality focuses on the<br />

silt and clay fraction which is not depthdependent.<br />

For bottom sediments it may be<br />

necessary to collect deposited sediments with<br />

minimum disturbance in order not to lose the<br />

fine material on the sediment surface, or because<br />

the vertical distribution of the sediment<br />

components is important.<br />

Turbidity measure with nephelometeric<br />

turbid meters is considered a good method for<br />

estimating suspension concentration in rivers<br />

(Lewis 1996).Measuring turbidity can be done<br />

by measured using either an electronic turbidity<br />

meter or handheld turbidity tube. Both methods<br />

28

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