A5     PROBLEM DEFINITION/BACKGROUND

 

In 1991, the Texas Legislature passed the Texas Clean River Act (Senate Bill 818) in response to growing concerns that water resource issues were not being pursued in an integrated, systematic manner.  The act requires that ongoing water quality assessments be conducted for each river basin in Texas, an approach that integrates water quality issues within the watershed.  The CRP legislation mandates that “each river authority (or local governing entity) shall submit quality-assured data collected in the river basin to the commission.” “Quality-assured data” in the context of the legislation means “data that comply with commission rules for surface water quality monitoring programs, including rules governing the methods under which water samples are collected and analyzed and data from those samples are assessed and maintained.” This QAPP addresses the program developed between the SRA and the TCEQ to carry out the activities mandated by the legislation.  The QAPP was developed and will be implemented in accordance with provisions of the Quality Management Plan for the Clean Rivers Program (most recent version). 

 

The purpose of this QAPP is to clearly delineate SRA QA policy, management structure, and procedures which will be used to implement the QA requirements necessary to verify and validate the surface water quality data collected. The QAPP is reviewed by the TCEQ to help ensure that data generated for the purposes described above are scientifically valid and legally defensible.  This process will ensure that data collected under this QAPP and submitted to the statewide database have been collected and managed in a way that guarantees its reliability and therefore can be used in water quality assessments and other programs deemed appropriate by the TCEQ.  Project results will be used to support the achievement of Clean Rivers Program objectives as contained in the Clean Rivers Program Guidance and Reference Guide FY 2008 -2009.

 

The SRA Environmental Services Division (ESD) collects surface water quality data as part of its commitment to water quality protection in the Sabine Basin.  This Water Quality Monitoring Program (WQMP) includes routine monitoring and analyses of physical, chemical, bacteriological, and biological parameters.  SRA also conducts special investigations concerning pollution complaints.

Additional monitoring requirements have been brought about through the implementation of the TCRP.  This additional systematic monitoring program complements the existing routine monitoring by providing information on the many subwatersheds not covered by the routine monitoring.  The systematic monitoring utilizes biological screening studies in combination with routine physical and chemical parameters to provide data on the health of aquatic life and long-range water quality protection.  The systematic monitoring also includes field investigations to provide data on subwatersheds, which have never been sampled.

 

The basin topography has been used to divide the Basin into 110 subwatersheds (24 of these are located in Louisiana), which are organized into 7 reaches.  A ‘reach’ of the main-stem of the River roughly corresponds to the old segment system but the reaches are based on hydrography and similarity of land features.  This system allows a manager to determine which areas have adequate water quality information and which areas do not.  The subwatershed approach also incorporates risk factors such as municipal and industrial outfalls, solid waste sites, urban and rural land use, etc., into the decision making process.

 

Water quality data is analyzed using the data analysis program developed by SRA following guidance from the TCEQ.  The Routine and Special Study Monitoring programs are reviewed each year to consider revisions in every aspect of the programs.

 

Monitoring plans were developed by the SRA and other monitoring partners in cooperation with TCEQ staff at the annual coordinated monitoring meetings.  Sampling for 24-hour dissolved oxygen monitoring will be conducted on a site in the Tenaha arm of Toledo Bend Reservoir and on one site in the Caddo Creek arm of Lake Tawakoni.

 

Additional sampling will be conducted under this QAPP by City of Longview personnel to provide data from sites not covered by the SRA sampling program. 

A6     PROJECT/TASK DESCRIPTION

 

SRA will conduct monitoring at routine monitoring sites to adequately characterize water quality trends and monitor progress in protecting or restoring water in the Sabine Basin.  All monitoring plans are coordinated with the TCEQ regional offices to avoid duplication of effort.  The routine monitoring sites include 44 sampling sites that are monitored monthly for routine physical and chemical parameters.  Selected sites are also monitored annually for metals in water.  Additional sites may be monitored for 24-hour dissolved oxygen parameters to determine aquatic life use support.  Details of the monitoring schedule, parameters, and sampling locations are included in Appendix B.

 

Routine monitoring will be conducted by the City of Longview at two sampling sites on Lake Cherokee.

 

See Appendix A for the project-related work plan tasks and schedule of deliverables for a description of work defined in this QAPP.  

 

See Appendix B for sampling design and monitoring pertaining to this QAPP.

 

 

Amendments to the QAPP

 

Revisions to the QAPP may be necessary to address incorrectly documented information or to reflect changes in project organization, tasks, schedules, objectives, and methods.  Requests for amendments will be directed from the SRA Project Manager to the CRP Project Manager electronically.  Amendments are effective immediately upon approval by the SRA Project Manager, the SRA QAO, the CRP Project Manager, the CRP Lead QA Specialist, and the CRP Project QA Specialist.  They will be incorporated into the QAPP by way of attachment and distributed to personnel on the distribution list by the SRA Project Manager.   

 

Special Project Appendices

 

Projects requiring QAPP appendices will be planned in consultation with the SRA and the TCEQ Project Manager and TCEQ technical staff.  Appendices will be written in an abbreviated format and will reference the Basin QAPP where appropriate.  Appendices will be approved by the SRA Project Manager, the SRA QAO, and the CRP Project Manager, the CRP Project QA Specialist, the CRP Lead QA Specialist and other TCEQ personnel as appropriate.  Copies of approved QAPPs appendices will be distributed by the SRA to project participants before data collection activities commence. 


A7     QUALITY OBJECTIVES AND CRITERIA

 

The purpose of routine water quality monitoring is to collect surface water quality data needed for conducting water quality assessments in accordance with TCEQ’s Guidance for Assessing Texas Surface and Finished Drinking Water Quality Data.  These water quality data, and data collected by other organizations (e.g., USGS, TCEQ, etc.), will be subsequently reconciled for use and assessed by the TCEQ.

 

Systematic watershed monitoring is defined by sampling that is planned for a short duration (1 to 2 years) and is designed to:  screen waters that would not normally be included in the routine monitoring program, monitor at sites to check the water quality situation, and investigate areas of potential concern.  Due to the limitations regarding these data (e.g., not temporally representative, limited number of samples, biological sampling does not meet the specimen vouchering requirements), the data will be used to determine whether any locations have values exceeding the TCEQ’s water quality criteria and/or screening levels (or in some cases values elevated above normal).  The SRA will use this information to determine future monitoring priorities.  These water quality data, and data collected by other organizations (e.g., USGS, TCEQ, etc.), will be subsequently reconciled for use and assessed by the TCEQ.

 

The measurement performance specifications to support the project purpose for a minimum data set are specified in Table A7.1 and in the text following.  The SRA laboratory will perform all of the analyses listed in Table A7.1.

Table A7.1 - Measurement Performance Specifications

 

PARAMETER

 

UNITS

 

MATRIX

 

METHOD

 

PARAMETER CODE

 

AWRL

 

Limit of Quantitation (LOQ)

 

PRECISION

(RPD  of LCS/LCSD)

 

BIAS

%Rec. of LCS

LOQ

CHECK STANDARD

%Rec

 

LAB

Field Parameters

 

pH

 

pH/ units

 

water

 

EPA 150.1 and TCEQ SOP, V1

 

00400

 

NA*

 

NA

 

NA

 

NA

 

NA

 

Field

 

DO

 

mg/L

 

water

 

SM 4500-O G and

TCEQ SOP, V1

 

00300

 

NA*

 

NA

 

NA

 

NA

 

NA

 

Field

 

Conductivity

 

uS/cm

 

water

 

EPA 120.1 and

TCEQ SOP, V1

 

00094

 

NA*

 

NA

 

NA

 

NA

 

NA

 

Field

 

Chlorine residual**

 

mg/L

 

water

 

SM 4500-Cl G and TCEQ SOP, V1

 

50060

 

NA

 

NA

 

NA

 

NA

 

NA

 

Field

 

Present Weather

 

1-clear

2-partly cloudy

3-cloudy

4-rain

5-other

 

NA

 

NA

 

89966

 

NA

 

NA

 

NA

 

NA

 

NA

 

Field

 

Salinity

 

ppt, marine only

 

water

 

SM 2520 and TCEQ SOP, V1

 

00480

 

NA*

 

NA

 

NA

 

NA

 

NA

 

Field

 

Temperature

 

°C

 

water

 

SM 2550 B and

TCEQ SOP V1

 

00010

 

NA*

 

NA

 

NA

 

NA

 

NA

 

Field

TDS,calculated

mg/L

water

calculation

70294

NA

 

 

NA

NA

NA

Field

 

Secchi Depth

 

meters

 

water

 

TCEQ SOP V1

 

00078

 

NA*

 

NA

 

NA

 

NA

 

NA

 

Field

 

Days since last

significant rainfall

 

days

 

NA

 

TCEQ SOP V1

 

72053

 

NA*

 

NA

 

NA

 

NA

 

NA

 

Field

 

Maximum pool width***

 

meters

 

water

 

TCEQ SOP V2

 

89864

 

NA*

 

NA

 

NA

 

NA

 

NA

 

Field

 

Maximum pool depth***

 

meters

 

water

 

TCEQ SOP V2

 

89865

 

NA*

 

NA

 

NA

 

NA

 

NA

 

Field

 

Pool length***

 

meters

 

water

 

TCEQ SOP, V2

 

89869

 

NA*

 

NA

 

NA

 

NA

 

NA

 

Field

 

% pool coverage***

 

%

 

water

 

TCEQ SOP V2

 

89870

 

NA*

 

NA

 

NA

 

NA

 

NA

 

Field

 

Total water depth

 

meters

 

water

 

TCEQ SOP V2

 

82903

 

NA*

 

NA

 

NA

 

NA

 

NA

 

Field

 

Flow

 

cfs

 

water

 

TCEQ SOP V1

 

00061

 

NA*

 

NA

 

NA

 

NA

 

NA

 

Field

 

Flow measurement method

 

1-gage

2-electric

3-mechanical

4-weir/flume

5-doppler

 

water

 

TCEQ SOP V1

 

89835

 

NA*

 

NA

 

NA

 

NA

 

NA

 

Field

 

Flow severity

 

 

 

 

1-no flow,

2-low,

3-normal,

4-flood,

5-high,

6-dry

 

water

 

 

 

TCEQ SOP V1

 

01351

 

NA*

 

NA

 

NA

 

NA

 

NA

 

Field

 

Wind Intensity

 

1-calm

2-slight

3-moderate

4-strong

 

water

 

 

 

NA

89965

 

NA*

 

NA

 

NA

 

NA

 

NA

 

Field

 

Water Surface

 

1-calm

2-ripples

3-waves

 

NA

 

NA

 

89968

 

NA

 

NA

 

NA

 

NA

 

NA

 

Field

 

Tidal Stage

 

1-low

2-falling

3-slack

4-rising

6-high

 

 

NA

 

NA

 

89972

 

NA

 

NA

 

NA

 

NA

 

NA

 

Field

 

Turbidity

 

NTU

 

water

 

SM 2130B-01

 

82079

 

.5

 

0.5

20

80-120

70-130

 

Field

 


 

 

24-hour Dissolved Oxygen Monitoring Parameters

 

Parameter

 

Units

 

Method

 

Parameter

Code

 

AWRL

 

Limit of Quantitation (LOQ)

 

 

PRECISION

(RPD  of LCS/LCSD)

 

Bias

% Rec

LCS

 

LOQ

Check

Standard

%Rec

 

Lab***

 

 

24-Hr D.O. Avg.

 

mg/l

 

TCEQ SOP, V1

 

89857

 

NA

 

NA

 

NA

 

NA

 

NA

 

field

 

Max Daily DO

 

mg/l

 

TCEQ SOP, V1

 

89856

 

NA

 

NA

 

NA

 

NA

 

NA

 

field

 

Min Daily DO

 

mg/l

 

TCEQ SOP, V1

 

89855

 

NA

 

NA

 

NA

 

NA

 

NA

 

field

 

# DO measurements during 24-Hrs

 

# meas.

 

TCEQ SOP, V1

 

89858

 

NA

 

NA

 

NA

 

NA

 

NA

 

field

 

24-Hr Avg. water Temperature

 

B Celsius

 

TCEQ SOP, V1

 

00209

 

NA

 

NA

 

NA

 

NA

 

NA

 

field

 

Max Daily water Temperature

 

B Celsius

 

TCEQ SOP, V1

 

00210

 

NA

 

NA

 

NA

 

NA

 

NA

 

field

 

Min Daily water Temperature

 

B Celsius

 

TCEQ SOP, V1

 

00211

 

NA

 

NA

 

NA

 

NA

 

NA

 

field

 

# water temp measurements during 24-Hrs.

 

# meas.

 

TCEQ SOP, V1

 

00221

 

NA

 

NA

 

NA

 

NA

 

NA

 

field

 

24-Hr Avg. Spec Conductance

 

uS/cm

 

TCEQ SOP, V1

 

00212

 

NA

 

NA

 

NA

 

NA

 

NA

 

field

 

Max Spec Conductance

 

uS/cm

 

TCEQ SOP, V1

 

00213

 

NA

 

NA

 

NA

 

NA

 

NA

 

field

 

Min Spec Conductance

 

uS/cm

 

TCEQ SOP, V1

 

00214

 

NA

 

NA

 

NA

 

NA

 

NA

 

field

 

# Spec Conductance measurements during 24-Hrs.

 

# meas.

 

TCEQ SOP, V1

 

00222

 

NA

 

NA

 

NA

 

NA

 

NA

 

field

 

Max Daily pH

 

Standard units

 

TCEQ SOP, V1

 

00215

 

NA

 

NA

 

NA

 

NA

 

NA

 

field

 

Min Daily pH

 

Standard units

 

TCEQ SOP, V1

 

00216

 

NA

 

NA

 

NA

 

NA

 

NA

 

field

 

# pH measurements during 24-Hrs.

 

# meas.

 

TCEQ SOP, V1

 

00223

 

NA

 

NA

 

NA

 

NA

 

NA

 

field

 

24-Hr Salinity Avg

 

ppt

 

TCEQ SOP, V1

 

00218

 

NA

 

NA

 

NA

 

NA

 

NA

 

field

 

Max Daily Salinity

 

 ppt

 

TCEQ SOP, V1

 

00217

 

NA

 

NA

 

NA

 

NA

 

NA

 

field

 

Min Daily Salinity

 

ppt

 

TCEQ SOP, V1

 

00219

 

NA

 

NA

 

NA

 

NA

 

NA

 

field

 

# salinity measurement during 24-Hrs

 

# meas.

 

TCEQ SOP, V1

 

00220

 

NA

 

NA

 

NA

 

NA

 

NA

 

field

 


 

 

PARAMETER

 

UNITS

 

MATRIX

 

METHOD

 

PARAMETER CODE

 

AWRL

 

Limit of Quantitation (LOQ)

 

PRECISION

(RPD  of LCS/LCSD)

 

BIAS

%Rec. of LCS

LOQ

CHECK STANDARD

%Rec

 

LAB

 

Conventional and Bacteriological Parameters

 

TSS

mg/L

water

SM 2540 D-97

00530

4

3

20

80-120

NA

SRA

 

Sulfate

mg/L

water

EPA 300.0, Rev. 2.1 (1993)

00945

5

5

 

20

80-120

70-130

 

SRA

 

Chloride

mg/L

water

EPA 300.0 Rev. 2.1 (1993)

00940

5

5

 

20

80-120

70-130

 

SRA

 

Chlorophyll-a,  spectrophotometric method

ug/L

water

EPA 446.0 Rev. 1.2

32211

3

3

 

20

80-120

NA

 

SRA

 

E. coli, IDEXX Colilert

MPN/100 mL

water

SM 9223-B

31699

1

1

 

.5****

NA

NA

 

SRA

 

Enterococcus, IDEXX Enterolert

MPN/100 mL

water

ASTM

D-6503

31701

1

1

 

0.5****

NA

NA

 

SRA

 

Ammonia-N, total

mg/L

water

EPA 350.1 Rev. 2.0 (1993)

00610

0.1

0.1

 

20

80-120

70-130

 

SRA

 

Nitrite-N

mg/L

water

EPA 300.0 Rev. 2.1 (1993)

00615

0.05

0.05

20

80-120

70-130

 

SRA

 

Hardness, total (as CaC03)

mg/L

water

SM 2340 C

00900

5

5

 

20

80-120

NA

 

SRA

 

Total Kjeldahl N

mg/L

water

EPA 351.2

 

00625

 

0.2

0.2

 

20

80-120

70-130

 

SRA

 

Nitrate-N, total

mg/L

water

EPA 300.0 Rev. 2.1 (1993)

00620

.05

0.05

 

20

80-120

70-130

 

SRA

 

O-phosphate-P

filter >15 min.

mg/L

water

EPA 300.0 Rev. 2.1

 

70507

.04

0.04

 

20

80-120

70-130

 

SRA

 

Total phosphorus-P

mg/L

water

EPA 365.4

00665

.06

0.06

 

20

80-120

70-130

 

SRA

 

 

Alkalinity, total

 

mg/L

 

water

SM 2320B

 

00410

 

20

20

20

NA

NA

 

SRA

 

TOC

 

mg/L

 

water

 

SM 5310 C

 

00680

 

2.0

 

1.0

NA

NA

NA

 

SRA

 

 

Metals

 

Aluminum, dis.

 

ug/L

 

water

 

EPA 200.8 Rev 5.4

(1998)

 

01106

 

200

 

25

 

20

 

80-120

 

70-130

 

SRA

 

 

Arsenic, dis.

 

ug/L

 

water

 

EPA 200.8 Rev 5.4

(1998)

 

01000

 

5

 

1

 

20

 

80-120

 

70-130

 

SRA

 

Barium, dis.

 

ug/L

 

water

 

EPA 200.8 Rev 5.4

(1998)

01005

1000

1

20

80-120

70-130

SRA

 

 

Cadmium, dis.

 

ug/L

 

water

 

EPA 200.8 Rev 5.4 (1998)

 

 

 

 

 

01025

 

.1

for waters <50 mg/L hardness

________

.3

for waters $50 mg/L hardness

 

0.1

 

20

 

80-120

 

70-130

 

SRA

 

 

Chromium, dis.

 

ug/L

 

water

 

EPA 200.8 Rev 5.4 (1998)

 

 

01030

 

10

 

0.1

 

20

 

80-120

 

70-130

 

SRA

 

 

Copper, dis.

 

ug/L

 

water

 

EPA 200.8 Rev 5.4 (1998)

 

 

 

 

 

 

01040

 

1

for waters <50 mg/L hardness

________

3

for waters $50 mg/L hardness

 

0.5

 

20

 

80-120

 

70-130

 

SRA

 

 

Lead, dis.

 

ug/L

 

water

 

EPA 200.8 Rev 5.4 (1998)

 

 

 

 

 

 

01049

 

.1

for waters <85 mg/L hardness

________

1

for waters $85 mg/L hardness

 

0.1

 

20

 

80-120

 

70-130

 

SRA

 

 

Nickel, dis.

 

ug/L

 

water

 

EPA 200.8 Rev 5.4 (1998)

 

01065

 

10

 

0.1

 

20

 

80-120

 

70-130

 

SRA

 

 

Selenium, total

 

ug/L

 

water

 

EPA 200.8 Rev 5.4 (1998)

 

01147

 

2

 

1

 

20

80-120

 

70-130

 

SRA

 

 

Silver, dis.

 

ug/L

 

water

 

EPA 200.8 Rev 5.4 (1998)

 

01075

 

.5

 

0.1

 

20

 

80-120

 

70-130

 

SRA

 

 

Zinc, dis.

 

ug/L

 

water

 

EPA 200.8 Rev 5.4 (1998)

 

01090

 

5

 

1

 

20

 

80-120

 

70-130

 

SRA

 

 


 

Benthics - Freshwater - Quantitative

 

PARAMETER

 

UNITS

 

MATRIX

 

METHOD

 

PARAMETER CODE

 

LAB***

 

Biological Data Reporting Units

 

1= number of individuals from subsample;

2 = number  of  individuals/ft2;

3 = number of individuals/m2;

4 = total number in kicknet

 

Water

 

TCEQ SOP, V2

 

89899

 

NA

 

Surber Sampler Effort, area sampled

 

m