Table 1: Sediment bioassay summary for Georgia Pacific Corporation

Bellingham, Washington (sampled September 1993)

Grabs/ Reps/

Site site site

 

Bioassay

DOE Type 1

t-test p Sig* error p

Dunnett's

ANOVA p F calc power test **

 

A-1

 

5

2 5

5

Rhepoxynius

Echinoderm

Neanthes

0.0101

0.0131

0.0990

_

_

0.1426

0.1855

0.3017

0.0793

0.0311

0.0020

(F 3, 15 = 2.75)

(F 4, 20 = 3.31)

(F 7, 32 = 4.26)

0.35

0.55

0.90

 

Different

Not different

 

A-2

 

1

Rhepoxynius

Echinoderm

Neanthes

 

 

 

 

 

 

 

 

 

 

 

 

 

 

 

A-3

4

1 5

5

Rhepoxynius

Echinoderm

Neanthes

0.0379

0.0035

0.0845

_

_

0.1426

0.1855

0.3017

0.0793

0.0311

0.0020

(F 3, 15 = 2.75)

(F 4, 20 = 3.31)

(F 7, 32 = 4.26)

0.35

0.55

0.90

 

Different

Not different

 

B-1

 

2 5

5

Rhepoxynius

Echinoderm

Neanthes

 

0.0124

0.0028

 

_

_

 

0.1855

0.3017

 

0.0311

0.0020

 

(F 4, 20 = 3.31)

(F 7, 32 = 4.26)

 

0.55

0.90

 

Different

Different

 

B-2

 

2

5

Rhepoxynius

Echinoderm

Neanthes

 

 

0.0020

 

 

_

 

 

0.3017

 

 

0.0020

 

 

(F 7, 32 = 4.26)

 

 

0.90

 

 

Different

 

B-3

 

2

5

Rhepoxynius

Echinoderm

Neanthes

 

 

0.0536

 

 

 

 

0.3017

 

 

0.0020

 

 

(F 7, 32 = 4.26)

 

 

0.90

 

 

Not different

 

C-1

5

3

5

Rhepoxynius

Echinoderm

Neanthes

0.0762

0.0010

 

 

_

0.1426

0.3017

0.0793

0.0020

(F 3, 15 = 2.75)

(F 7, 32 = 4.26)

0.35

0.90

 

 

Different

 

C-2

 

2

Rhepoxynius

Echinoderm

Neanthes

 

 

 

 

 

 

 

 

 

 

 

 

 

 

 

C-3

 

2 5

5

Rhepoxynius

Echinoderm

Neanthes

 

0.0256

0.0278

 

_

_

 

0.1855

0.3017

 

0.0311

0.0020

 

(F 4, 20 = 3.31)

(F 7, 32 = 4.26)

 

0.55

0.90

 

Different

Not different

Total statistically significant 10 of 14 7 of 14

* Sig means difference based on results of t-tests. An x means a statistically significant difference was found

** Dunnett's test evaluates statistical differences between bioassays for test and reference sediments.

Different means a statistically significant difference exists between test and reference sediments.

Not different means a statistical difference does not exist.

Statistical model for alternate design related to sediment sampling

Model: o = l + P i + D j + PD i j + r ( ij ) k

P = Position (upcurrent or downcurrent) ( i = 1..2, fixed)

D = Distance (from start of diffuser) ( j = 1..5, fixed)

r = replicates ( k = 1..4, random)

Source df EMS F

P i 1 u 2r + 20 l P MSP / MSr (1, 30)

D j 4 u 2r + 8 l D MSD / MSr (4, 30)

PD ij 4 u 2r + 4 l P D MDPD / MSr (4, 30)

r ( ij ) k 30 u 2r

total 39

 

 

REPLICATION OF BIOASSAYS (PTI, 1991)

The guidelines for all of the sediment bioassays included in this document recommend that all field-collected sediments be homogenized before subsamples are removed for bioassay and chemical analyses. This technique is the one used for most studies in Puget Sound, and it ensures that the bioassay and chemical results are related as closely as possible. The replicate analyses that are subsequently conducted on the bioassay subsample assess the variability encountered in laboratory testing, rather than the variability of sediment toxicity that exists in the field. To assess field variability, an alternate sampling design could be specified that requires each bioassay replicate to be run on a separate replicate grab sample from each station. The primary drawback to this technique is that the single set of chemical concentrations usually measured at each station (i.e., primarily because of cost constraints) would not relate directly to the sediment toxicity measured in each replicate grab sample. This lack of a direct relationship between bioassay and chemical results can sometimes make data interpretation difficult for individual replicate samples. However, the mean bioassay response could be compared directly with chemical concentrations if the chemical measurements are made on a composite of equal amounts of sediment subsampled from each of the replicate samples used for bioassay analysis. (emphasis added)

 

Sections of SEDIMENT MANAGEMENT STANDARDS

(Chapter 173 - 204) that contain directives to use t-tests

(State of Washington, 1992)

WAC 173 - 204 - 320 Marine sediment quality standards

WAC 173 - 204 - 420 Sediment impact zone maximum criteria

WAC 173 - 204 - 520 Cleanup screening levels criteria

Example from WAC 173 - 204 - 320 (3) Biological effects criteria

(emphasis added)