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appendix b final 2008 biological surveys of los angeles and long ...

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2.0 Water Quality<br />

2.0 WATER QUALITY<br />

2.1 INTRODUCTION<br />

This section presents the results <strong>and</strong> key findings <strong>of</strong> water quality measurements conducted<br />

within the Ports <strong>of</strong> Los Angeles <strong>and</strong> Long Beach during July <strong>2008</strong>. Methods used for water<br />

quality measurements are described in Section 2.2. Results <strong>of</strong> water quality measurements are<br />

provided in Section 2.3. Discussions <strong>of</strong> spatial patterns <strong>and</strong> comparisons with historical<br />

conditions are provided in Sections 2.4 <strong>and</strong> 2.5, respectively.<br />

The water quality parameters measured consisted <strong>of</strong> temperature, salinity, dissolved oxygen<br />

(DO), acidity/alkalinity (pH), <strong>and</strong> light transmittance/water clarity (transmissivity). Temperature<br />

<strong>and</strong> salinity are st<strong>and</strong>ard hydrographic measures used to characterize different water masses.<br />

These can be important in a port/harbor setting that receives freshwater flows from storm drains<br />

<strong>and</strong> other watershed input sources. DO, pH, <strong>and</strong> transmissivity are key water quality indicators<br />

for the protection <strong>of</strong> beneficial uses, as defined in the Basin Plan <strong>and</strong> California Ocean Plan.<br />

For example, human activities can result in reductions in DO concentrations <strong>and</strong> water clarity<br />

<strong>and</strong>/or alter pH, which causes adverse effects on <strong>biological</strong> resources. However, it is important<br />

to note that these water quality parameters also reflect natural physical, chemical, <strong>and</strong> <strong>biological</strong><br />

processes that can result in changes at tidal, daily (diurnal), seasonal, <strong>and</strong> <strong>long</strong>er (decadal) time<br />

periods. Thus, water quality data typically are evaluated in the context <strong>of</strong> deviations from<br />

natural or background conditions.<br />

2.2 METHODOLOGY<br />

Water quality sampling was<br />

conducted during the July (summer)<br />

<strong>2008</strong> survey. Water quality<br />

characteristics were measured as<br />

continuous vertical pr<strong>of</strong>iles at each<br />

<strong>of</strong> 29 stations, 15 stations in the Port<br />

<strong>of</strong> Los Angeles <strong>and</strong> 14 in the Port <strong>of</strong><br />

Long Beach (Figure 2.2-1).<br />

Sampling for Station LA14 was<br />

conducted at two locations<br />

(designated i <strong>and</strong> o), for inner <strong>and</strong><br />

outer Consolidated Slip, to match<br />

historical sampling locations. Station<br />

coordinates <strong>and</strong> water depths are<br />

listed in Table 2.2-1. Water depths<br />

for the stations ranged from 4 to 25 meters [m] (13 to 82 feet [ft]).<br />

Sampling was conducted during a one-day survey on July 30, <strong>2008</strong>. The survey was conducted<br />

from a rigid hulled inflatable vessel. A Lowrance Model S-337C DF (Dual Frequency)<br />

differential GPS was used for navigation <strong>and</strong> vessel positioning. All stations were sampled<br />

while live-boating (i.e., vessel was not anchored during the casts).<br />

Each <strong>of</strong> the water quality parameters was measured as continuous vertical pr<strong>of</strong>iles using a<br />

Seabird model SBE19 Conductivity Temperature Depth (CTD) instrument with additional pH<br />

<strong>and</strong> DO probes <strong>and</strong> a SeaTech CST-714PR, 0.25-centimeter (cm) pathlength transmissometer.<br />

All instruments were factory calibrated at SeaBird Electronics, Inc., in Bellevue, WA, prior to the<br />

survey.<br />

<strong>2008</strong> Biological Surveys <strong>of</strong> Los Angeles <strong>and</strong> Long Beach Harbors 2–1<br />

April 2010

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