|
CICEET Progress Report for the period 8/01/00
through 1/31/01
Project Title:
Sediment Recycling: Marsh Renourishment Through Dredged Material
Disposal
Principal Investigator(s):
Lynn A. Leonard,
Martin H. Posey,
Troy D. Alphin,
Lawrence B. Cahoon,
Richard A. Laws
- Accomplishments
- Scheduled Tasks:
- Vascular plant surveys conducted in August 2000, October
2000, and January 2001.
- Preliminary analyses of vascular plant data collected
from May 2000 to Januray 2001.
- Winter water level surveys conducted from January 15th
- February 15th, 2001.
- Soil geochemistry measurements collected in August,
October and December 2000.
- Preliminary analyses of soil geochemistry measurements.
- Conducted first six-month "post sediment placement"
sediment trap survey in December 2000.
- Benthic biomass samples collected monthly from August
to December 2000.
- Analysis of benthic biomass samples collected from February
to June 2000.
- Collection of microalgal taxonomy samples in August
and October 2000.
- Preparation and processing of microalgal samples for
taxonomy.
- Benthic invertebrate core processing and identification
in progress.
- Presented overview of the project as part of another
CICEET funded project "Estuaries Live!". This was a joint
effort facilitated by Dr. John Taggert of the NCNERR and
Ms. Susan Lovelace also of NCNERR. We broadcast our overview
live from the field via internet links. The North Carolina
Coastal Resources Commission and several "on-line" elementary
schools were the primary audience.
- Progress on Task
As described in earlier progress reports, project initiation
and data collection were delayed due to the permitting process
required by North Carolina State law. Since project initiation,
however, data collection and analyses have generally proceeded
on schedule. Exceptions are described in the "difficulties
encountered" section below
- Difficulties Encountered
Very few difficulties have been encountered during the
last six-months of the project. Our biggest problem has
been a changeover in project personnel that has hindered
our progress in completing the microalgal taxonomy portion
of the project. In July 2000, the graduate student who
had been working on this part of the project transferred
to another institution. We have not been able to find
a replacement to conduct these analyses and, at this time,
are relying on undergraduate research assistants. Unfortunately,
it has taken more time than expected to train these students
to prepare and process the samples. Another difficulty
has been site access using powered jon-boats. To alleviate
this problem, we purchased a canoe which can be used to
access the sites even at very low tides.
- Anticipated Success in Meeting Project Objectives in
Scheduled Project Period
Because initiation of our project was delayed due to the
NC state permitting process, we applied for and were granted
a no-cost extension to this project. We are confident that
we will easily and successfully meet the project objectives
within the revised project period.
- Preliminary data
Vascular Plant Data
Vascular plant data have been collected bi-monthly since
June 2000. Preliminary plant density data are summarized in
Figure 1. In general, stem densities in the deteriorated sites
are lower than those in the non-deteriorated sites. There
appears to be no relationship between stem density and treatment,
however, these results have not yet been examine statistically.
As expected, the number of live shoots per meter square decreased
in the winter. We expect that any relationship between thickness
of added sediment and plant density will not be apparent until
well into the summer 2001 growing season.
Sediment Traps
Sediment deposition data collected using petridish sediment
traps are shown in Table 1 (see Tables.xls). Mean sediment
deposition data collected in October 2000 are shown in Figure
2. In general, deposition in deteriorated sites following
placement of dredged material exceeds deposition in non-deteriorated
sites. This same trend existed prior to sediment placement.
Accumulation in the deteriorating sites following sediment
placement has risen one order of magnitude over levels observed
prior to fill placement. It is our contention that these measurements
actually reflect sediment mobility rather than sediment accumulation.
The higher rates observed in October may be due to background
seasonal trends in sediment mobility associated with canopy
die-back. Note that control values (areas not treated with
sediments) also show an increase in sediment accumulation
at this time. Within the deteriorated sites, areas overlain
by the greatest thickness of dredged material show the lowest
sedimentation rates. This may indicate that the increase in
sediment grain size associated with sediment placement has
decreased sediment mobility in these sites.
 |
Sediment Geochemistry
Redox potentials have been measaured bi-monthly in each
of the three treatment areas within each of the four sample
plots since August 2000. Additional measurements have been
collected in the control areas. The Eh profiles are shown
in Figure 3. In general, the sediments have become more oxygenated
at all sites between August and December 2000. Sediment placement
appears to have had the greatest impact near the surface in
the deteriorated sites when compared to the control. These
data are still be analyzed.
Water Level
Four RDS WL-40 water level recorders have been placed in
each of the four treatment sites. Each instrument measures
and records water level once every six minutes. The instruments
were deployed in early January and have not yet been retrieved
from the field. Preliminary water level data will be included
in the next six-month progress report.
Benthic Biomass
Benthic biomass samples have been taken at all project sites
and analyzed for benthic chlorophyll production. Preliminary
data are shown in Figure 4. Monthly sample collection was
conducted for the four months prior to the addition of the
dredged material. After the addition of dredged material,
samples were taken twice a month during the months of May,
June, July, and August 2000. Since August 2000, samples have
been collected monthly. Benthic chlorophyll samples are taken
using a 2.5cm diameter coring tube that collects approximately
20 mm of sediment. Samples are then frozen until analysis
for benthic chlorophyll can be completed. Samples through
June of 2000 have been analyzed.
Microalgal taxonomy
Accomplishments to date are shown in Table 2. The table
shows all of the samples collected thus far and the state
of preparation for each sample. Some samples have been prepared
to the slide stage and are awaiting microscopic analysis.
Other samples are still in the cleaning stage (e.g. October
set). Two more sets of samples will be collected: one in the
week of Feb. 19, 2001, and one set in early April depending
on suitable tides. Those two sample sets will basically complete
the one year sampling cycle because the first post sediment
emplacement samples were collected in late May and early June,
2000.
| |
Table 2. CICEET Microalgal Samples |
|
|
|
|
| |
|
|
|
|
|
| DATE |
SAMPLE # |
CLEANED |
SETTLED |
SLIDE |
COUNT |
| |
|
|
|
|
|
| 01/22/00 |
DET-I-A |
X |
X |
X |
|
| |
DET-I-B |
X |
X |
X |
|
| |
DET-I-C |
X |
X |
X |
|
| |
DET-II-A |
X |
X |
X |
|
| |
DET-II-B |
X |
X |
X |
|
| |
ND-III-A |
X |
X |
X |
|
| |
ND-III-B |
X |
X |
X |
|
| |
ND-IV-A |
X |
X |
X |
|
| |
|
|
|
|
|
| 04/08/00 |
DET-I-A |
X |
X |
|
|
| |
DET-I-B |
X |
X |
X |
|
| |
DET-I-C |
X |
X |
X |
|
| |
DET-II-A |
X |
X |
X |
|
| |
DET-II-B |
X |
X |
|
|
| |
DET-II-C |
X |
X |
X |
|
| |
ND-III-A |
|
|
|
|
| |
ND-III-B |
X |
X |
|
|
| |
ND-III-C |
X |
X |
|
|
| |
ND-IV-A |
X |
X |
|
|
| |
ND-IV-B |
X |
X |
X |
|
| |
ND-IV-C |
X |
|
|
|
| |
|
|
|
|
|
| 05/20/00 |
DET-I-A |
No samples for this date because sediment
emplacement for these sites did not occur until 5-19 and 5-26. |
| |
DET-I-B |
| |
DET-I-C |
| |
DET-I-D |
| |
DET-II-A |
| |
DET-II-B |
| |
DET-II-C |
| |
DET-II-D |
| |
ND-III-A |
X |
X |
X |
|
| |
ND-III-B |
X |
X |
|
|
| |
ND-III-C |
NO |
SAMPLE |
|
|
| |
ND-III-D |
X |
X |
|
|
| |
ND-IV-A |
X |
X |
X |
|
| |
ND-IV-B |
X |
X |
|
|
| |
ND-IV-C |
X |
X |
X |
|
| |
ND-IV-D |
X |
X |
|
|
| |
|
|
|
|
|
| 06/01/00 |
DET-I-A |
X |
X |
X |
|
| |
DET-I-B |
X |
X |
X |
|
| |
DET-I-C |
X |
X |
X |
|
| |
DET-I-D |
X |
X |
|
|
| |
DET-II-A |
X |
X |
X |
|
| |
DET-II-B |
X |
X |
X |
|
| |
DET-II-C |
X |
X |
X |
|
| |
DET-II-D |
X |
|
|
|
| |
ND-III-A |
|
|
|
|
| |
ND-III-B |
X |
X |
X |
|
| |
ND-III-C |
X |
X |
|
|
| |
ND-III-D |
X |
X |
X |
|
| |
ND-IV-A |
X |
X |
|
|
| |
ND-IV-B |
|
|
|
|
| |
ND-IV-C |
X |
|
|
|
| |
ND-IV-D |
|
|
|
|
| |
|
|
|
|
|
| 06/07/00 |
DET-I-A |
X |
X |
X |
|
| |
DET-I-B |
X |
X |
X |
|
| |
DET-I-C |
X |
X |
X |
|
| |
DET-I-D |
X |
|
|
|
| |
DET-II-A |
X |
X |
|
|
| |
DET-II-B |
X |
|
|
|
| |
DET-II-C |
X |
|
|
|
| |
DET-II-D |
X |
X |
X |
|
| |
ND-III-A |
X |
X |
|
|
| |
ND-III-B |
X |
|
|
|
| |
ND-III-C |
X |
X |
|
|
| |
ND-III-D |
X |
X |
|
|
| |
ND-IV-A |
X |
|
|
|
| |
ND-IV-B |
X |
|
|
|
| |
ND-IV-C |
X |
|
|
|
| |
ND-IV-D |
X |
X |
X |
|
| |
|
|
|
|
|
| 06/15/00 |
DET-I-A |
X |
X |
X |
|
| |
DET-I-B |
X |
X |
X |
|
| |
DET-I-C |
X |
X |
X |
|
| |
DET-I-D |
X |
X |
X |
|
| |
DET-II-A |
X |
X |
X |
|
| |
DET-II-B |
X |
X |
X |
|
| |
DET-II-C |
X |
X |
X |
|
| |
DET-II-D |
X |
X |
X |
|
| |
ND-III-A |
X |
X |
X |
|
| |
ND-III-B |
X |
X |
X |
|
| |
ND-III-C |
X |
X |
X |
|
| |
ND-III-D |
|
|
|
|
| |
ND-IV-A |
X |
X |
X |
|
| |
ND-IV-B |
X |
|
|
|
| |
ND-IV-C |
X |
|
|
|
| |
ND-IV-D |
X |
X |
X |
|
| |
|
|
|
|
|
| 08/04/00 |
DET-I-A |
X |
|
|
|
| |
DET-I-B |
X |
|
|
|
| |
DET-I-C |
X |
|
|
|
| |
DET-I-D |
X |
|
|
|
| |
DET-II-A |
X |
|
|
|
| |
DET-II-B |
X |
|
|
|
| |
DET-II-C |
X |
|
|
|
| |
DET-II-D |
X |
|
|
|
| |
ND-III-A |
X |
|
|
|
| |
ND-III-B |
X |
|
|
|
| |
ND-III-C |
X |
|
|
|
| |
ND-III-D |
X |
|
|
|
| |
ND-IV-A |
X |
|
|
|
| |
ND-IV-B |
X |
|
|
|
| |
ND-IV-C |
X |
|
|
|
| |
ND-IV-D |
X |
|
|
|
| |
|
|
|
|
|
| 10/09/00 |
DET-I-A |
X |
|
|
|
| |
DET-I-B |
X |
|
|
|
| |
DET-I-C |
X |
|
|
|
| |
DET-I-D |
X |
|
|
|
| |
DET-II-A |
X |
|
|
|
| |
DET-II-B |
X |
|
|
|
| |
DET-II-C |
X |
|
|
|
| |
DET-II-D |
X |
|
|
|
| |
ND-III-A |
X |
|
|
|
| |
ND-III-B |
X |
|
|
|
| |
ND-III-C |
X |
|
|
|
| |
ND-III-D |
X |
|
|
|
| |
ND-IV-A |
X |
|
|
|
| |
ND-IV-B |
X |
|
|
|
| |
ND-IV-C |
X |
|
|
|
| |
ND-IV-D |
X |
|
|
|
Benthic invertebrates
Benthic infaunal samples were collected six weeks following
the addition of sediment. This delay allowed some degree of
site recovery due to the actual sediment addition process.
While processing of these samples continues preliminary data
shows some potentially interesting patterns. Predicted impacts,
to infauna, varied based on the amount of sediment to the
added. Minimal impacts were predicted for the areas with the
least sediment addition while more negative impacts were predicted
for areas with larger sediment addition. However even within
samples from the "thick" sediment additions we have
found infaunal assemblages. While we cannot at this time say
what numerical impact sediment addition had on infauna, we
do know sediment additions did not defaunate the underlying
substrate.
- Tasks and activities for next reporting period
- Tasks for the next reporting period:
- Extend boardwalks at sampling sites
- Identication of areas with the potential for channelization.
- Place "Hogs Hair" filters over low areas to prevent
channelization
- Continue bi-monthly vascular plant surveys and begin
statistical analysis of results
- Conduct summer water level measurements
- Continue bi-monthly geochemical measurements and statistical
analysis of results
- Conduct second six-month "post sediment placement" sediment
trap survey
- Collect sediment samples for examination of 6-month
granulometry changes
- Conduct textural and compositional analyses on sediment
samples
- Continue to collect monthly benthic biomass samples
- Continue laboratory analysis of benthic biomass samples
and conduct statistical analyses
- Complete microalgal sampling and sample preparation
for year 1
- Begin microscopic analyses for microalgal taxonomy (i.e.
species identification and counting)
- Initiate statistical analyses once all samples have
been counted
- Continued processing and analysis of benthic infaunal
samples.
- Collection of the second set of benthic infaunal samples
from all, for evaluation of recovery following a major
period of recruitment.
- Work plan to accomplish tasks
Sampling of various parameters described above will be
conducted according to the schedule of tasks provided.
The project currently employs two graduate students and
two undergraduate students who assist with data collection,
sample preparation, and analyses. One additional graduate
student, currently funded on a Teaching Assistantship
by UNCW, also works 10-15 hours per week on the project.
Some of the preliminary results will be presented at
the Southeastern Sectional meeting of the Geological Society
of America in Raleigh in April 2001. One of the graduate
students funded by the project (A. Croft) will be giving
the presentation entitled: "Effects of Dredged Material
Disposal on Salt Marsh Processes".
- Concerns or difficulties
As we approach the summer season, our greatest concern
is site security. Last year, we felt that the edges of the
sites were somewhat compromised by non-project personnel
who visited the site. We have taken steps to reduce visibility
of the site to nearby boaters and also taken steps to mitigate
any damage near the site caused by curious onlookers (e.g.
placed hogs-hair filters where vegetation has been trampled
etc.).
- Expenditures
Expenditures were slightly less than anticipated for the
work accomplished to date.
|