Nutrient Loading in Coastal Streams, Variation with Land Use in the
Carpinteria Valley
Timothy H. RobinsonBren School of Environmental Science and Management
University of California Santa Barbara
Introductions
Overview
Creeks of the Carpinteria Valley:
• Arroyo Paredon• CSM North Tributaries • Santa Monica• Franklin• Carpinteria/Gobernador• Lagunitas
My research project:
•Nutrient export•Modeling•Predictions
Watersheds Drainage Area Max-Elevation Ave-Slope Urban Agriculture Chaparral/Forest
(km2) (m) (ft) (%) (%) (%) (%)Carpinteria 39.2 1424 4672 38 2 11 85
Franklin 11.6 533 1749 20 29 30 40Santa Monica 9.8 1192 3911 45 3 3 93
Methodology
Identify land use classes and sampling site locations: Chaparral/Forest, Avocado, Greenhouse, Open-Field Nursery, Residential and Commercial
Sampling strategies: Subcatchment, point discharge and above-below
Sampling methods: Manual sample or ISCO auto-sampler
GIS database development
Data analysis
Nutrient flux calculation (hydrology and stream chemistry)
Nutrient export coefficient model development
Integration with an urban growth model
Sampling Site Locations
Measuring Nutrient Concentrations
Grab samples and ISCO auto- samplers
Analyzing for: Ammonium (NH4
+), Nitrate (NO3-), Total Dissolve
Nitrogen (TDN), Phosphate (PO43-), Total Particulate
Carbon (TPC), Total Particulate Nitrogen (TPN), Total Particulate Phosphate (TPP), Total Suspended Sediments (TSS) and major ions at selected locations
Specifics:
Frequency: • Regular sampling:
Once every 2 weeks during the dry seasonOnce a week during the wet season
Storm sampling:Every hour on the rising limb of the hydrographEvery 2-4 hours on the falling limb of the hydrograph
Project duration: WY2001, WY2002 and WY2003
Measuring Stream Flow
Staff Gauges and Pressure TransducersSurveying the Cross-Sections
Developing Rating Curves
Stream Chemistry and Hydrology
0
300
600
900
1200
10/30 10/31 11/1
Nit
rate
(µ
M)
0.6
0.8
1.0
1.2
1.4
Sta
ge
at
ou
tle
t (f
t)
outlet
commercial
residential
chaparral/forest
stage-recorded
Carpinteria Creek (WY-2002)
General Trends in Nutrient Concentrationsby Watershed
1
10
100
1000
10000
Franklin Carpinteria Santa Monica
nit
rate
(µ
M)
baseflow
stormflow
1
10
100
Franklin Carpinteria Santa Monica
ph
osp
hat
e (µ
M)
baseflow
stormflow
Nutrient LoadingDevelopment of a Nutrient Flux Model
StreamChemistry
ObservedStage
PTStage
(5-min)
ObservedFlow
PTFlow
(5-min)
StreamChemistry
Stage-Discharge Relationship(HEC-RAS)
Flow(hourly)Flow
(hourly)
StreamChemistry(hourly)
Identify: Baseflow, Peakflow..
Nut. Conc.
Flow(hourly)
StreamChemistry
(model/obs)
Nut. Flux(conc/flow)
AnnualAnnualNutrient LoadingNutrient Loading
ObservedFlow
(hourly)
Linear extrapolation
1
10
100
1000
10000
5-Jan 15-Jan 25-Jan 4-Feb 14-Feb 24-Feb 6-Mar
cum
ula
tive
exp
ort
(Km
ol)
0
50
100
150
200
250
flo
w (
cfs)
NH4 NO3 PO4
TDN flow
WY 2001
Cumulative Nutrient ExportFranklin Creek Watershed
Cumulative Nitrate ExportNursery Site
0
20
40
60
80
100
120
140
160
180
10/26 11/5 11/15 11/25 12/5 12/15 12/25
Cu
mu
lati
ve
Ex
po
rt (
Km
ol)
0
20
40
60
80
100
120
Flo
w (
cfs
)
NO3-FK07
NO3-FK06
Flow-FK07
Flow-FK06
0
2,000
4,000
6,000
8,000
10,000
12,000
Santa Monica Franklin Carpinteria
Nu
trie
nt
Lo
adin
g (
kg/y
r)
NH4-N
NO3-N
DON-N
PO4-P
WY2001 Basin Outlet Mass Flux
WY 2001
Comparison of Flux afterNormalizing with Runoff
1
10
100
Oct. 30 Nov. 29 Dec. 20
Date of Storms
Ex
po
rt (
g/h
a-m
m)
NO3-residentialNO3-commercial
NO3-greenhouse
0
1
10
100
1000
Oct. 30 Nov. 29 Dec. 20
Date of Storms
Ex
po
rt (
g/h
a-m
m)
PO4-residential
PO4-commercial
PO4-greenhouse
AAGISGISEE
IIInterviewInterview
IILiteratureLiterature
KKLiteratureLiterature
LUE tkeK
kk ttD/VD/V
LULUGISGIS
Abbreviation key:• E – Export Coefficient Function• B – Watershed Response Variable• S – Soils• P - Precipitation
Nutrient Export Coefficient Model
DKIAEL atmiiii
DDatmatm
LTERLTER
DDatmatmLiteratureLiterature
S+P +ASMCS+P +ASMC
• ASMC – Antecedent Soil Moisture Content• K – Down Stream Distance-Decay Function• k + – Coefficients• t – Time
• D – Distance Traveled Downstream• V – Average Velocity Traveled Downstream
L
Integration with an Urban Growth Model (SLEUTH)
• SLEUTH : an urban growth model implemented for the Santa Barbara area that predicts future land use, example 2050
• Enables comparison of future loadings to standards being set for stream water quality regulations (TMDLs)
• Evaluation of proposed BMP mitigations
Significance of the Project
Presentations:• PhD Seminar, Bren School UCSB• Santa Barbara Coastal LTER Seminar, UCSB• University of California Toxic Substances Research & Teaching Program, Annual Symposium, Long Beach• Coastal Water Resources, American Water Resources Association 2002 Spring Conference, New Orleans• Southern California Wetlands Recovery Project, 2002 Symposium, Ventura• California and the Worlds Oceans 02 Conference, Santa Barbara
Questions
Thank you!!
Sampling Teams
Three teams sampling in and around storm events1. Lower reach sites2. Upper reach sites3. Restricted sites
Percentage Land Use Class by Land Use Sub-Area
LU Site Area PercentCode Code (hectares) 1 2 3 4 5 6 20 50 60 Impervious*
1 GB04 1873.2 100 0 0 0 0 0 0 0 0 01 CP05 1210.2 100 0 0 0 0 0 0 0 0 02 CP02 746.9 42.1 36.2 1.3 2.3 0 3.7 12.0 0.1 2.1 7.45 CP30 6.0 0 0 0 0 100 0 0 0 0 30.06 CP20 31.9 9.2 0 0 0 0 90.8 0 0 0 77.24 FK06 80.4 11.9 20.6 4.1 47.4 0 1.5 14.5 0 0 11.43 FK04 16.9 2.9 0 97.1 0 0 0 0 0 0 68.01 SM05 901.6 100 0 0 0 0 0 0 0 0 0
* Land use codes and associated percentage of impervious surfaces**.LU-Code % Imp Class:
1 0 Undeveloped - Chaparral/Forest **2 5 Avocados - out buildings3 70 Greenhouse Small Watersheds, Technical Release 55, 4 10 Nursery Washington, DC, 19865 30 Medium density residential 2. US Army Corps of Engineers. 2000. HEC-HMS6 85 Commercial Technical Manual Hydrologic Engineering 20 10 Other agriculture Center, Davis, Ca, pp. 12350 100 Open w ater 3. Interpretation by T.H. Robinson and R.E. Beighley 60 0 Forested Riparian
% Area of Land Use (LU-Code)*:
References for percentage of impervious 1. Soil Conservation Service, Urban Hydrology for
Santa Monica Debris Basin
Gobernador Debris Basin
Chaparral/Forest Sites
Santa Monica Carpinteria Gobernador(µM) SM05 CP05 GB05NH4Min: 0* 0* 0*Max: 0.6 2.7 1.1
Average: 0.2 1.1 0.4NO3Min: 0* 1.7 0*Max: 2.0 17.0 26.9
Average: 0.5 8.4 4.5TDNMin: 0* 10.0 4.8Max: 14.9 53.5 55.5
Average: 8.6 25.0 18.1PO4Min: 0.6 0.5 0.3Max: 8.6 9.6 7.4
Average: 3.8 3.7 4.0* At or below the detection limit.
CP05
SM05
GB05
Residential Site(CP30)
Commercial Site(CP20)
Greenhouse SiteGreenhouse Site
Nursery Site(FK06+FK07)
0
5
10
15
20
25
30
35
40
45
50
10/30 10/31 11/1
Ph
os
ph
ate
(µ
M)
0.6
0.8
1.0
1.2
1.4
Sta
ge
@ o
utl
et
(ft)
outlet
commercial
residential
chaparral/forest
stage-visual
stage-recorded
Getting to Know Your Local Streams
CarpinteriaCreek
(first storm)
0
300
600
900
1200
10/30 10/31 11/1N
itra
te (
µM
)0.6
0.8
1.0
1.2
1.4
Sta
ge
at
ou
tle
t (f
t)
outlet
commercial
residential
chaparral/forest
stage-visual
stage-recorded
0
5
10
15
20
25
30
35
40
45
50
10/30 10/31 11/1
Ph
os
ph
ate
(µ
M)
0.6
0.8
1.0
1.2
1.4
Sta
ge
@ o
utl
et
(ft)
outlet
commercial
residential
chaparral/forest
stage-visual
stage-recorded
CP00 – outletCP20 – commercialCP30 – residentialGB04 – chaparral/
forest
Franklin Creek
(first storm)
0
40
80
120
160
30-Oct 31-Oct 1-Nov
Ph
osp
hat
e (µ
M)
0.0
0.2
0.4
0.6
0.8
1.0
1.2
Sta
ge
at
ou
tle
t (f
t)
outlet
below greenhouse
greenhouse
stage - visual
stage - recorded
316 µM
0
1000
2000
3000
4000
5000
30-Oct 31-Oct 1-Nov
Nit
rate
(µM
)
0.0
0.2
0.4
0.6
0.8
1.0
1.2
Sta
ge
at o
utl
et (
ft)
outlet
below greenhouse
greenhouse
stage - visual
stage-recorded