observations and modeling of narragansett bay nutrient...
TRANSCRIPT
Observations and modeling of Narragansett Bay nutrient dynamics:
Do we run the west coast offense?
Presenters: Chris Kincaid & Kevin Rosa, Graduate School of Oceanography, University of Rhode Island Colleagues: Scott Nixon, David Ullman, Steve Granger, URI-GSO
R. Wally Fulweiler, Boston University
Anna Pfeiffer-Herbert, Richard Stockton University
Rhode Island Coastal Waters: Narragansett Bay & Rhode Island Sound East Coast Offense: Nutrients from watershed Urbanized Higher runoff West Coast Offense: Nutrients from shelf Lower runoff
Narragansett Bay
Marthas Vineyard
Rhode Island Sound (RIS)
Inner shelf
Providence
Block Is.
Buzzards Bay
L. I. Sound
Greenwich Bay
Providence River
Focus on Watershed Nutrients to Narragansett Bay Estuary
West Passage
River nutrients: Northern Blackstone River Pawtuxet River Woonasquatucket/Moshas. Eastern Taunton River
Blackstone
Mt. Hope Bay KEY PT. SOURCES: WWTFs or
waste-water treatment facilities Fields Pt. & Bucklin Pt. (NBC)
Fall River
Providence
Greenwich Bay
Providence River
Connecting Circulation > Nutrients > Water Quality
West Passage
Blackstone
Mt. Hope Bay
Fall River
Providence
Greenwich Bay
Edgewood Shoal
Chronic Low Oxygen Regions
Seekonk R.
Red = hypoxia
http://www.geo.brown.edu/georesearch/insomniacs/
FULLBAY ROMS
Tilt Current Meters Laboratory
Utilize a 3-legged stool approach to
Coastal circulation
e.g. Edgewood Shoals Region
ROMS Numerical Model Regional Ocean Modeling System Scaled Physical Model Spatial-Temporal Observations
Tilt Current Meters Lagrangian Drifters
Bottom-mounted ADCP
Ship-mounted ADCP
Circulation Data
20 Years of Bay Data: Circles=BM-ADCPs
Lines=Shipmounted-ADCPs
Yellow regions = 10-25 TCMS
20 Years of Bay Data: Counterclockwise residual flow
Up east, Out west Impacted embayments
Retention gyres Reduced flushing
METHOD 3: Computer Models
Input Forcing: Tides Runoff Winds Air Temperature Water Density (Salt, Temp.)
ROMS Model Solves Equations: Conserve Mass Momentum Conserve Energy / Salt
ROMS 3. Output: 4-D Flow & Salt/Temp. Transport Todays talk (a) Chemical Dyes (b) Ecosystem Processes
ROMS Cases. Terrestrial (East-coast) nutrient dynamics
-January – September 2010
-River discharge (USGS), Winds (PORTS), Tides (ADCIRC), Atmospheric (reanalysis-NARR) , rain (TF Green).
-Blackstone River nutrients (Pt. & Non-Pt.) UMass Blackstone River Water Quality Model ( P. Rees, Mass Water Resourses Res. Center).
-Pawtuxet River nutrients - NBC data.
-Other rivers: empirical flow vs. nutrients model (from UMass model).
-WWTF nutrients (data from plant managers and hypothetical levels)
(1) Nutrients as passive chemical dye advection/diffusion only Dye sources supplying low-DO areas?
(2) ROMS NPZD Model N=nutrients, P=phytoplankton, Z=zooplankton, D=detritus
Factors controlling phytoplankton biomass?
Case 1 Case 2
Forcing files detail
16 Distinct Dyes 9 Rivers 7 WWTFs 1) How each dye through system? 2) Flushing vs. accumulation? 3) Cost/benefit of WWTF (nutrient) reduction strategies?
Mosh/Woon
Blackstone (Pt. vs. Non Pt.)
Palmer
Taunton
2 Greenwich Bay Rivers
GB WWTF
Fields Pt. WWTF
Bucklin Pt. WWTF
Pawtuxet
WWTF
Fall River WWTF
EP-WWTF
10-Mile
Hunt
Case 1
Shoal
Channel
Chemical Dye from Fields Pt. WWTF: Focus on upper Providence River
Red = Dimensionless Concentration of 1
Dye from Fields Point WWTF: Transport examples
Plume in outflow jet Plume entrained in shoal gyre Plume flushed
(near-surface) Blackstone River Dye: Repeatable Mid-Bay Transport Paths
1. West Passage: Weak wind SW-ward wind
2. Greenwich Bay Intrusion: Seabreeze NW-ward wind
3. East Passage Strong NE-ward wind
Greenwich Bay?
Nitrogen Contributors to Greenwich Bay: SPRING HIGH FLOW (+30days)
1) Blackstone, 2) Pawtuxet , 3) Fields Pt, 4) Taunton, 5) Internal
41% 20%
24%
2. Greenwich Bay
Late Summer – August, 2010
Blackstone
Pawtuxet
Greenwich Bay
From east From north
Greenwich Bay? Nitrogen to Greenwich Bay Late Summer 2010: 1) Internal , 2) Blackstone, 3) Fields Pt, 4) Pawtuxet
Variable with season, runoff, wind
41% 20%
24%
2. Greenwich Bay
Late Summer – August, 2010
Greenwich Bay
Edgewood Shoals Bottom Water
Near-bottom Taunton Dye in Providence River
Taunton Dye
Conclusions: Dye Transport Patterns Complex.
Northern sources variable down-bay paths.
Accumulations in impacted areas vary seasonally (winds, runoff)
Counterclockwise residual flow & layered estuarine flow: eastern & southern dyes to impacted northern areas.
Second set of ROMS Models: ROMS NPZD Ecosystem Model
Z=zooplankton Also Detritus Equation
N= Total nitrogen
P=phytoplankton
Uptake rate
Light penetration term
Multiple runs: Uptake rate, light extinction, grazing, mortality, WWTF levels
Nitrogen not a conservative dye.
Start with focus on bay-wide bloom, June, 2010
Total Nitrogen: Surface Reference case: Vm2.5, KL0.75, ZG1.0 . Contours in milli-Mole/m^3 (divide by 75 to get to mg/l).
50 mM/m^3 Transport oscillations:
Northern nutrients
1) down East Passage,
2) down West Passage.
3) pumped into Greenwich Bay Wind, tide, runoff controls
a)
Total Nitrogen Contours: (near-surface, summer 2010) Mid-Bay Transport Paths Similar to Dye
Transport oscillations:
Northern nutrients
1) down East Passage,
2) down West Passage.
3) pumped into Greenwich Bay Wind, tide, runoff controls
Providence River N. Prudence S. Prudence Lower Bay
Fundamental observation in Bay: TN reduction from Seekonk to Mouth of Providence River
All runs (pre-bloom) have TN match basic observation:
1. 40% reduction Head of Prov. River to Mouth
2. Seekonk 50% higher than upper Prov. River
See
kon
k R
iver
Tota
l Nit
roge
n
Latitude
Phytoplankton Contours: (early summer bloom 2010)
RED= 20 mM m-3
Day 165 (June 14)
SURFACE BOTTOM
Initiate Mid-bay and migrate northward
Surface Phytoplankton Contours: (early summer bloom 2010)
RED= 20 milli-M m-3
Day 165 (June 14)
Movie: Bloom starts mid-Bay Moves northward
Greenwich Bay
Phillipsdale
DATA
Large uptake rate, more light
Slow uptake rate, more light
Fast uptake rate, less light
Modeled bloom matches a) nutrient magnitudes, b) mid-Bay start, c) timing of northward march
Ph
yto
pla
nkt
on
Co
nc.
, mM
/m3
0
20
40
WWTFs @ 5, 3 & 0 mg/mL
Plots from mid-Bay: North Prudence
Phytoplankton bloom intensity vs. parameters:
3. different WWTF releases levels
1. ecosystem parameters (uptake, light, death)
2. environmental factors
Variations In Wind
Eliminate Greenwich Bay
Change Light Extinction
Changing Growth Rate
Dif
fere
nce
in T
ota
l B
loo
m M
agn
itu
de
Difference in
Integrated Bloom Magnitude over 10 days
= -
ROMS Case A ROMS Case B
Absolute value
Use differential-integrated phytoplankton bloom index to quantify relative sizes of a) environmental factors and
b) managed nutrient changes c) NPZD parameters (uptake, light, grazing)
Variations In Wind
Eliminate Greenwich Bay
Change Light Extinction
Changing Growth Rate
Dif
fere
nce
in T
ota
l B
loo
m M
agn
itu
de
Difference in
Integrated Bloom Magnitude over 10 days
= -
ROMS Case A ROMS Case B
If big difference then blooms very to sensitive to this parameter
Absolute value
Use differential-integrated phytoplankton bloom index to quantify relative sizes of a) environmental factors and
b) managed nutrient changes c) NPZD parameters (uptake, light, grazing)
3 v
s. 0
Variations In Wind
Eliminate Greenwich Bay
Change Light Extinction
Changing Growth Rate
Dif
fere
nce
in T
ota
l B
loo
m C
on
cen
trat
ion
Use differential-integrated phytoplankton bloom index to quantify relative sizes of a) environmental factors and
b) managed nutrient changes c) NPZD parameters (uptake, light, grazing)
WWTFs nutrient release levels at 0 mg/L versus 3 mg/L
0 v
s 3
3
vs
5
5 v
s 1
5
Variations In Wind
Eliminate Greenwich Bay
Change Light Extinction
Changing Growth Rate
Dif
fere
nce
in T
ota
l B
loo
m C
on
cen
trat
ion
Bigger difference 5 mg/L vs. 15 mg/L WWTF releases, factor of 10
3 t
o 0
Medium Growth Rate
5 t
o 3
15
to
5
Variations In Wind
Eliminate Greenwich Bay
Change Light Extinction
Changing Growth Rate
Changing WWTF Nutrient Outputs
Dif
fere
nce
in T
ota
l B
loo
m C
on
cen
trat
ion
Higher phytoplankton uptake rate, 15 to 5 mg/l change in WWTF release, bigger impact
Higher Growth Rate
3 t
o 0
5 t
o 3
15
to
5
Medium Growth Rate
High Growth Rate
Eliminate Greenwich Bay
Change Light Extinction
Changing Growth Rate
Changing WWTF Nutrient Outputs
Dif
fere
nce
in T
ota
l B
loo
m C
on
cen
trat
ion
Sou
thea
stw
ard
N
ort
hw
estw
ard
N
ort
hea
stw
ard
So
uth
wes
twar
d
Variations In Wind
Compare changes in applied prevailing wind to a reference case of no-wind. Natural effect of wind changes has similar impact as 15 to 5 mg/l WWTF change
3 t
o 0
5 t
o 3
15
to
5
3 t
o 0
5 t
o 3
15
to
5
Medium Growth Rate
High Growth Rate
Variations In Wind Change
Light Extinction
Changing Growth Rate
Changing WWTF Nutrient Outputs
Dif
fere
nce
in T
ota
l B
loo
m C
on
cen
trat
ion
Sou
thea
stw
ard
No
rth
wes
twar
d
No
rth
east
war
d
Sou
thw
estw
ard
Med
ium
to
Hig
h
Low
to
Med
ium
Changes in light penetration parameter larger impact on integrated total bloom than managed (e.g. 5mg/l to 3/mg/l) nutrient reductions from WWTFs.
3 t
o 0
5 t
o 3
15
to
5
3 t
o 0
5 t
o 3
15
to
5
Medium Growth Rate
High Growth Rate
Variations In Wind Change
Light Extinction
Changing Phytoplankton Uptake Rate Changing
WWTF Nutrient Outputs
Dif
fere
nce
in T
ota
l B
loo
m C
on
cen
trat
ion
Sou
thea
stw
ard
No
rth
wes
twar
d
No
rth
east
war
d
Sou
thw
estw
ard
Med
ium
to
Hig
h
Low
to
Med
ium
Low
to
Me
diu
m
Med
ium
to
Hig
h
Phytoplankton uptake rate key parameter for integrated total bloom
3 t
o 0
5 t
o 3
15
to
5
3 t
o 0
5 t
o 3
15
to
5
Conclusions:
Order of factors controlling bloom size 1) Ecosystem parameters (growth, light, etc) 2a) Environmental parameters (winds) 2b) 15 to 5 mg/l drop in WWTF releases 3) 5 to 3 mg/l drop in WWTF releases
Relative importance of shelf (RIS) nutrients for Bay ecosystem?
Narragansett Bay
Marthas Vineyard
Rhode Island Sound (RIS)
Inner shelf
Providence
Block Is.
Buzzards Bay
L. I. Sound Scott Nixon, first week of work,
“let’s test how DIN from shelf gets into Bay”
Bath
ymetry (m
)
BM-ADCPS
Ship-Mounted ADCP
Building RIS Data Sets / Models RISG, Endeavor Prog.
1) 1999-2001 led by Scott Nixon 2) Recent 2005, 2009-2011, 2016
Drifter Study (x3)
Coastal Current
Strong in summer
Into RIS from SE, exit to SW Weak interior flow Summer stratification RIS to Bay Intrusions!!
1. Colors show 3 deployment sites: Solid line=3m; Dashed=6m
2. Drifters Retained in Vineyard Sound
3. Drifters ride coastal current to Bay
13 Days
May 23
June 3
Drifter Patch: In ~ 5/23/2016 midnight. Plot 6/5 noon.
4. Whats up, central RIS?
Nixon, Granger, Fulweiler and others Series of ”intensive” cruises (RISG) Narragansett Bay to RIS (99-01)
Temperature, salinity, nutrient surveys
RIS
Mt. Hope Bay
Mid-Bay High
Production Zone
Greenwich Bay
Providence River
a)
North South
RIS
BAY
BAY
DIN: 7 mg/L
1 mg/L
T=16°
T=10°
Temperature
RIS
BAY
Interface
?
Average Summer Conditions
DIN
RIS
Mt. Hope Bay
Mid-Bay High
Production Zone
Greenwich Bay
Providence River
a)
BAY
East Passage TRANSECT
West Side
East Side
INFLOW OUTFLOW
1999-2001: 17 Full tide cycle ship-mounted ADCP cruises Mouth-interface region of Bay – RIS Winter/summer residual (or subtidal) exchange similar
East Passage ADCP Sub-tidal flow
Looking north D
epth
, m
35m
Nixon: “Is deep RIS DIN an important source for Bay?
3800 meters
1300 meters
RIS a)
1999-2001: 3 moored ADCPs. East Passage, West Passage, RIS
2007: 3 BM-ADCPs East/West Pass. 2008: 2 BM ADCPs RIS
Northward Inflow
Sub
tid
al F
low
, cm
/s 18
0
0 2 4 6 8 -2
Low
er E
ast
Pass
., 2
00
0
Mean
ADCP Shows Wind-driven Intrusion
Surface
Mid
Bottom
Days since wind event, 5/20/2000
Northward wind
Southwestward wind
Wind-driven intrusion
Two Modes of RIS to Bay Flow (Pfeiffer-Herbert et al, 2015)
1) Mean residual (non-tidal) inflow to East Passage (3-5 cm/s)
2) 5-15 Wind-driven intrusions per summer
>1000 CMS 200,000 M of DIN per day
Mode 1: ”Steady” inflow 1000 CMS 200K Moles DIN per day
Mode 2: Large wind-driven inflow
>7000 CMS
7 million Moles DIN/event
a)
b)
Coastal Current HIGH DIN
RIS DEEP
Pump station
Mixed-up RIS DIN?
Subtidal flow x Height x Width x DIN = Intrusion #
Moored ADCP Data
Underway ADCP Estimates
Nixon Data
EPSCOR Funding RISG Funding
50 m
30 m
3 H
ose
inta
kes
In-line sensors, pumps, controls
East
West Side
East Side
7 mg/L?
Moored ADCPs
? mg/L ?
West Side
East Side INFLOW
OUTFLOW Lower East Passage ADCP Sub-tidal flow
Looking north
Pump station & ADCPs. Firm up Volume flux & Chemical flux vs. time
Lower East Passage
ROSA: Ongoing work, ROMS Modeling & Analysis of existing data sets Supply pathways RIS water/nutrients to Narragansett Bay. Background/steady intrusions Wind-induced, large scale intrusions High energy exchange events (Floyd).
Shelf Intrusions
Persistent trickle from Periphery Current
2-7 day wind events
Quick, Extreme events
1. ADCP under the Newport Bridge during the storm a. This is a good test of model performance: captured both the bottom
temperature and the vertical structure of the currents.
Hurricane Floyd
ADCP
∆z = 2 m
H = 40 m
T
http://cdn.onlyinyourstate.com/wp-content/uploads/2016/04/Aerial_view_of_Claiborne_Pell_Newport_Bridge_-_01-700x501.jpg
The ROMS model
RIVERS
WIND
HEAT, FRESHWATER
The ROMS model
Storm landfall
4°C drop
Bottom temperature time series
Cool, high-DIN shelf-water?
Bottom temperature time series
Bottom temperature: data vs. model
Quantifying post-storm intrusion: data only
Assessing model skill
ADCP Observations
Quantifying post-storm intrusion: data vs. models
Assessing model skill
ADCP Observations
ROMS No Stratification
Quantifying post-storm intrusion: data vs. models
Assessing model skill
ADCP Observations
ROMS No Stratification
ROMS WITH STRATIFICATION
Quantifying post-storm intrusion: data vs. models
Assessing model skill
The barotropic (constant-density) model does not predict the strong shelf-water inflow
Drifter movie 2: Effects of Stratification
Density cross-sections
Drifter movie 3: Storm vs. No Storm
Estimated Input Volume for the 4 days following Floyd:
Rivers:
5 x 107 m3
East Passage:
5 x 108 m3 (USGS Data)
(ROMS model)
Storm landfall
Bottom temperature time series
ADCIRC operational model: Forecasting inundation from Irma
ADCIRC operational model: Forecasting inundation from Irma
This ocean model is invaluable for informing
evacuations
but its simplified physics can’t predict
nutrient transports or ecosystem impacts.
1. Hazardous Chemical spills a. Extent of oil spills from Hurricanes Katrina and Rita is still being
assessed
Hurricanes: After the storm surge
http://www.nbcnews.com/id/10838641/ns/us_news-katrina_the_long_road_back/t/oil-company-katrina-spill-victims-got-m/
1. Chemical spills a. Extent of oil spills from Hurricanes Katrina and Rita is still being assessed
http://www.nola.com/katrina/index.ssf/2010/08/extent_of_oil_spills_from_2005_hurricanes_is_still_being_assessed.html
2. Nutrient intrusions, plankton blooms, hypoxia a. Roman et al. (2006) “Chesapeake Bay Plankton and Fish Abundance
Enhanced by Hurricane Isabel Hurricane” b. Li et al. (2006) “Hurricane-induced storm surges, currents and
destratification in a semi-enclosed bay”
http://ripr.org/post/quahog-fisherman-pleased-progress-narragansett-bay-cleanup#stream/0 http://cdn.newsday.com/polopoly_fs/1.10821124.1441758504!/httpImage/image.JPG_gen/derivatives/display_600/image.JPG
Hurricanes: After the storm surge
<<TAKE-AWAYS>>
1. Goal: modeling storm events as realistically as possible.
2. Presenting results from a regional 3D baroclinic modeling that is forced by a 2D storm surge model.
a. Find that even under strong winds, baroclinic (stratification-driven) effects are critical.
3. Argue that this model is well-suited for studying water mass exchanges.
a. Volume of shelf-water input on order 10x greater than sum of all rivers.
Hurricane Floyd
1. Catastrophic flooding in eastern US, particularly North Carolina
a. 15’ storm surge in Long Beach, NC
2. 11” of rain in parts on New England
3. RI experienced increased river flows but minimal storm surge and only about 3” of rain.
https://www.weather.gov/images/mhx/19990916/Rain1.jpg
Wind Wind Wind
Warm
Cool
Well- Mixed
Wind Wind Wind
Intermediate
Intermediate
Partially Stratified
z y
Shouldn’t vertical mixing lead to warmer bottom water?
Sea surface height and northward deep velocity
Assessing model skill