Listing Methodology Listing Methodology Aquatic Life q Prepared - - PowerPoint PPT Presentation

listing methodology listing methodology aquatic life q
SMART_READER_LITE
LIVE PREVIEW

Listing Methodology Listing Methodology Aquatic Life q Prepared - - PowerPoint PPT Presentation

Listing Methodology Listing Methodology Aquatic Life q Prepared for the 303(d) Listing Methodology Meeting P d f h 303(d) Li i M h d l M i Wednesday, September 3, 2014 EDU contacts: Kristy Richardson, Scott Garncarz, and Sarah Wheeler


slide-1
SLIDE 1

Listing Methodology Listing Methodology Aquatic Life q

P d f h 303(d) Li i M h d l M i Prepared for the 303(d) Listing Methodology Meeting Wednesday, September 3, 2014

EDU contacts: Kristy Richardson, Scott Garncarz, and Sarah Wheeler (Listing Methodology) (Listing Methodology) and Chris Theel (MMI and bug guru)

PHOTO: http://communityscience.org/volunteer/biological-monitoring/

slide-2
SLIDE 2

Policy 10.1 List ing Met hodology y

Provides quantitative assessment method for

g gy

Provides framework for interpreting MMI threshold determining attainment of

aquatic life use

p g into regulatory outcome Offers guidance on factors Utilizes numeric thresholds based on expected/reference Offers guidance on factors which may influence listing decision such as spatial and biological conditions (and their variability) temporal distribution of samples Accounts for warm-water/cold- water and class distinctions Includes process for adding and removing water body from 303(d) li Protects against large declines 303(d) list

slide-3
SLIDE 3

Hist orical perspect ive

2016 – Policy 10-1 revision

process

2014 – LM workgroup to re-

address issues from 2012 and any

  • thers

process

2012

LM k di d

2013 – WQCD recommended

and WQCC adopted extension of Policy 10-1 through 2016

  • thers

2012 – LM workgroup discussed

issues; not addressed because LM was cancelled

2010 – Policy 10-1 adopted

slide-4
SLIDE 4

Aquatic life use Aquatic life use attainment

A quick review of the MMI as an assessment tool to determine aquatic life use attainment for rivers and streams as described in streams, as described in Policy 10.1

slide-5
SLIDE 5

What is an MMI? What is an MMI?

Multi-metric Index - a combination of metrics (eg. richness,

composition tolerance) that are responsive to stress composition, tolerance) that are responsive to stress, ecologically meaningful and offer diverse and non-redundant community information y

Predator & Predator & shredder shredder taxa taxa % Mayflies % Mayflies taxa taxa Beck’s Beck’s biotic biotic index index

MMI MMI score score (biotype (biotype 2) 2)

Total Total taxa taxa Clinger Clinger taxa taxa

slide-6
SLIDE 6

What is a Biot ype? What is a Biot ype?

  • predictor variables are used to assign site to a biotype group

Stream Stream l Site Site slope slope Level IV Level IV

Biotype Biotype

Site Site elevation elevation Level IV Level IV ecoregion ecoregion

1:transition 1:transition 2: mountains 2: mountains 3 l i & 3 l i & 3: plains & 3: plains & xeric xeric

slide-7
SLIDE 7

Met hod for assessing aquat ic Met hod for assessing aquat ic life use at t ainment

Quantitative Quantitative assessment of assessment of bi l i l bi l i l Determine Determine bi t bi t Comparison Comparison with biotype with biotype-

  • ifi

ti ifi ti biological biological condition condition biotype biotype specific aquatic specific aquatic life threshold life threshold

Collect & preserve bugs

biotype 1 (transition) biotype 2 (mountains) Use EDAS to calculate biotype-specific MMI then compare to threshold Identify and count bugs biotype 3 (plains & xeric)

slide-8
SLIDE 8

MMI as measuring st ick

Range of MMI scores for Range of MMI scores for reference/expected reference/expected

MMI as measuring st ick

p conditions conditions

MMI

100

MMI ->

Attainment Impairment Attainment Impairment Impairment threshold Biotype Attainment threshold 42 1 (transition) 52 42 2 (mountains) 50 22 3 (plains & xeric) 37

slide-9
SLIDE 9

Prot ect ion of diverse biot a and Prot ect ion of diverse biot a and sensit ive species

The Basic Standards (Reg. 31) classifies waters differently based on the whether the water is capable of sustaining a based on the whether the water is capable of sustaining a wide variety of biota, including sensitive species

Class 1 waters are capable of sustaining a wide variety Class 2 waters are not capable of sustaining this variety Class 2 waters are not capable of sustaining this variety

slide-10
SLIDE 10

MMI as measuring st ick

Range of MMI scores for Range of MMI scores for

MMI as measuring st ick

g reference/expected reference/expected conditions conditions

100

MMI ->

Attainment (class 2) Attainment Impairment The grey zone ( l 1) (class 1)

slide-11
SLIDE 11

Class 1 wat ers - t he grey zone Class 1 wat ers t he grey zone met rics

Biotype Hilsenhoff Biotic Index Shannon Diversity Index

1 (transition) < 5.4 > 2.4 2 (mountains) < 5.1 > 3.0 3 (plains & xeric) < 7.7 > 2.5

  • Pass both metrics -> attainment
  • Pass one metric only -> impairment
  • Pass neither metric -> impairment
slide-12
SLIDE 12

Prot ect ion of high scoring wat ers Prot ect ion of high scoring wat ers

Range of MMI scores for Range of MMI scores for g reference/expected reference/expected conditions conditions

100

MMI ->

>64 high scoring water Attainment Impairment 22

Year 1 Year 2

>22

slide-13
SLIDE 13

Flowchart: MMI Comparison

MMI Output (Single or Duplicate samples)

wit h Aquat ic Life Thresholds

adapted from Policy 10-1, Figure 1

samples) Single or Average MMI Scores

Duplicate

Single or Duplicate sample?

Single

Class I

  • r II?

g Class I

Assess MMI score against attainment threshold for appropriate biotype Does MMI exceed attainment threshold? Is MMI less than impairment threshold? No Assess MMI score against attainment I i t

Class II

Yes No Yes against attainment threshold for appropriate biotype Do both auxiliary metrics pass? Assess HBI and Shannon Diversity Index metrics against auxiliary Impairment Yes No metrics pass? g y metric thresholds for appropriate biotype Attainment Is MMI less than impairment threshold? Yes No

slide-14
SLIDE 14

Problems and S

  • lut ions

Problems and S

  • lut ions

1.Extension of Sampling season 1.Extension of Sampling season

PROBLEM STATEMENT: Policy 10-1 defines the index period for

sampling as July 1 – Oct. 1, however, there are circumstances when samples collected outside the index period are representative and should be included in period are representative and should be included in assessments due to return flows, irrigation releases, etc.

SOLUTION: The Division will include samples collected within a SOLUTION: The Division will include samples collected within a

few weeks after the recommended sampling season index period for assessments on a case by case basis.

slide-15
SLIDE 15

Problems and S

  • lut ions

Problems and S

  • lut ions
  • 2. Aquatic life samples that differ in
  • 2. Aquatic life samples that differ in

attainment

PROBLEM STATEMENT: Policy 10-1 is not clear about how the

Division will assess streams that have differing MMI scores in th t ti t the same representative segment.

SOLUTION: If two different MMI scores are assessed for the same SOLUTION: If two different MMI scores are assessed for the same

calendar year and both are determined to be representative, then the segment will be place on the M&E List. If differing MMI scores are assessed for different calendar years then most MMI scores are assessed for different calendar years, then most recent representative score will be used for listing decisions.

slide-16
SLIDE 16

MMI2012 - attainment

2012

M&E MMI impairment M&E List 303(d) List No Listing MMI2012 - impairment MMI2013 - impairment MMI2011 - impairment

slide-17
SLIDE 17

Problems and S

  • lut ions

Problems and S

  • lut ions
  • 3. Inconsistencies with Sediment Policy
  • 3. Inconsistencies with Sediment Policy

PROBLEM STATEMENT: With the adoption of Policy 10-1, the

Policy 98-1 has some inconsistencies in regards to aquatic life assessment.

SOLUTION: The Division will review sediment data and MMI scores

and make listing decisions independently.

slide-18
SLIDE 18

Problems and S

  • lut ions

Problems and S

  • lut ions
  • 3. Inconsistencies with Sediment Policy

S di t P li A ti Lif (MMI) C l i

  • 3. Inconsistencies with Sediment Policy

Sediment Policy Aquatic Life (MMI) Conclusion

attainment impairment listed for aquatic life impairment attainment listed for sediment impairment impairment listed for aquatic life p p q listed for sediment

slide-19
SLIDE 19

Problems and S

  • lut ions

Problems and S

  • lut ions
  • 4. High Quality Water Drop
  • 4. High Quality Water Drop

PROBLEM STATEMENT: Policy 10-1 outlines how high scoring

segments will be considered impaired if MMI scores drop over 22 points. The policy does not, however, explain what constitutes attainment after the segments have been listed due constitutes attainment after the segments have been listed due to the drop.

SOLUTION Th Di i i

ill id t i tt i t if

SOLUTION: The Division will consider a segment in attainment if

MMI scores improve by a minimum of half of the original decline and exceed attainment thresholds.

slide-20
SLIDE 20

Recovery of high scoring wat ers Recovery of high scoring wat ers

100

MMI ->

>64 high scoring water Attainment Impairment

24 Year 1 Year 2 Decline > 22 points 24 ≤12 Year 3+

slide-21
SLIDE 21

Recovery of high scoring wat ers Recovery of high scoring wat ers

100

MMI ->

>64 high scoring water Attainment Impairment

40 Year 1 Decline > 22 points 40 ≤20 Year 2 Year 3+

slide-22
SLIDE 22

Recovery of high scoring wat ers Recovery of high scoring wat ers

Class 1 or class 2 waters?

Class 2 Class 1

100

MMI ->

Class 1

>64 high scoring water Attainment Impairment

50 Year 1 Decline > 22 points 50 ≤25 Year 2

The grey zone (class 1)

Asses against gray zone metrics Year 3+

(class 1)

slide-23
SLIDE 23

Problems and S

  • lut ions

Problems and S

  • lut ions
  • 5. Portioning
  • 5. Portioning

PROBLEM STATEMENT: Policy 10-1 does not include language that

explains how a portion of a segment could be listed if the MMI sample does not represent the entire segment.

SOLUTION: Portioning for aquatic life using MMI scores will be

decided on a case-by-case basis following Section D(6)b of the Listing Methodology and must include representative samples Listing Methodology and must include representative samples within the same sampling index period.

slide-24
SLIDE 24

No Listing Listing MMI2012 - attainment M&E List List MMI2012 - impairment 303(d) ( ) List

Assumption: Like hydrological conditions

slide-25
SLIDE 25

Problems and S

  • lut ions

Problems and S

  • lut ions
  • 6. Multiple subsampling
  • 6. Multiple subsampling

PROBLEM STATEMENT: The Division has determined that there are specific

cases where multiple subsampling and the resulting averaging of MMI scores is appropriate

SOLUTION: Multiple subsampling may be used when the entire single

sample exceeds 360 individuals and one of the following cases applies: 1) The total number of taxa in a single macroinvertebrate sample 1) The total number of taxa in a single macroinvertebrate sample exceeds 45. 2) The dominance of one individual taxon exceeds 75% of the total count in a single macroinvertebrate sample

A subsample as defined in t he cont ext of t he Colorado MMI, is a procedure t o reduce t he individual organism count of a whole sample exceeding 360 individuals, t o a st andardized 300 fixed organism count bet ween 240 and 360 individuals.

slide-26
SLIDE 26

Quest ions/ Comment s? Quest ions/ Comment s?

Kristy Richardson@state co us CONTACT INFORMATION: Kristy.Richardson@state.co.us Scott.Garncarz@state.co.us Sarah.Wheeler@state.co.us

slide-27
SLIDE 27

Flowchart:

Collect i t

Mult iple subsampling

inverts Does the sample contain >360 individuals? Y No Does the sample contain >45 taxa? Generate MMI Yes Yes contain >45 taxa? Subsample x10 Generate 10 MMI Calculate Average MMI No Is one taxon >75%

  • f the sample?

Yes No