Comparison of Total Phosphorus and Macro Invertebrates and the Impact of Land Use on Water Quality. Laura Roldán Isardo Braverman Puerto Rico

Similar documents
Impact of an Agricultural Point Source on Macroinvertebrate Communities and Water Quality on the Lamoille River

Acidity and Alkalinity:

Habitat and Macroinvertebrate Assessment in San Pablo Creek. Karyn Massey

The Snapshot CONODOGUINET CREEK WATERSHED SNAPSHOT

EUTROPHICATION. Student Lab Workbook

PINEY RUN WATERSHED 2005 PROFILE

Water Quality in the Upper Cohansey Watershed

A Claytor Nature Center Stream Monitoring Experience

Water Quality in the Rat River St.Malo Watershed:

River of Ashe County, NC

Redwood Shores Lagoon August Monthly Water Quality Monitoring Report

Redwood Shores Lagoon November 2016 Monthly Water Quality Monitoring Report

Redwood Shores Lagoon February 2019 Monthly Water Quality Monitoring Report

Water Quality Testing

Appendix X: Non-Point Source Pollution

Redwood Shores Lagoon May 2017 Monthly Water Quality Monitoring Report

Jackson Lake Analysis

Eutrophication: Tracing Nutrient Pollution Back to Penns Creek

RESPONSE OF THE BENTHIC MACROINVERTEBRATE COMMUNITY IN THREE PIEDMONT STREAMS IN NORTH CAROLINA TO LAND USE CHANGES OVER A 20 YEAR PERIOD.

National Aquatic Monitoring Center (NAMC): Protocol for the Collection of Aquatic Macroinvertebrate Samples

Otonabee Region WATERSHED

Mecklenburg County Land Use & Environmental Services Agency; 2

Aquatic Species Diversity and Water Quality

River Monitoring and Water Resource Terms

How is Water Quality Affected by Land Use?

CLMP+ Report on Grass Lake (Anoka County) Lake ID# CLMP+ Data Summary

Grants Pass Water Quality Monitoring

Factsheet: Town of Deep River Water Quality and Stormwater Summary

Land Use, Water Quality, and Biotic Community Attributes

REPORT. Report No: 2013/0958 Prepared For: Natural Resources Committee Prepared By: Dean Olsen, Environmental Resource Scientist Date: 11 July 2013

Factsheet: City of West Haven Water Quality and Stormwater Summary

Gray s Creek. Gray s Creek

Water Quality indicators and How Human Activities Affect Water Quality

Benthic Macroinvertebrates and MS4

Environmental Services

Factsheet: Town of East Lyme Water Quality and Stormwater Summary

Maitland Valley WATERSHED

SAN BERNARD RIVER ABOVE TIDAL - SEGMENT 1302

Environmental Services

Mock Stream Habitat Assessment: Bringing the outside in!

Stormwater Management in Your Backyard: Stormwater 101

Water Chemistry Monitoring

Maine Biological and Nutrient Criteria. Tom Danielson and Dave Courtemanch Maine DEP

Summary of Basin Characteristics and Facilities. General Land-use Characteristics: Withdrawal and Discharge Sites: Sampling Site Statistics:

WASA Quiz Review. Chapter 2

Follow this and additional works at:

Biotic Factors to Monitor Water Quality

Total Maximum Daily Load Development for Unnamed Tributary to Pitts Creek. Public Meeting March 26, Why Are We Here

Stormwater Management Tools: Real-Life Solutions for a Resilient Community Riparian Corridor Protection

How Sensitive Are They?

Vancouver Watershed Health Assessment. Burnt Bridge Creek Watershed

Water Quality. New Standards on the Way? by Marty P. Lamia and Albert R. Capellini, P.E., BCEE

Background Information

Linda Cooper, Eno River State Park, Durham, NC

Factsheet: Town of Trumbull Water Quality and Stormwater Summary

Goose Creek Watershed Assessment Summary October 2003

LSR Issue Summary. 1. Water Quality. Technical Input Nutrient enrichment

Factsheet: Town of Hamden Water Quality and Stormwater Summary

Jordan River Watershed Council STREAM FUNCTION INDEX (SFI)

Land Use Activities Potential Pollution Problems. Land Disposal septic system bacteria, nitrate, phosphate

Water Quality Results from Indian Head River, Hanover, MA

GULF OF MEXICO - SEGMENT 2501

CLMP+ Report on Fleming Lake (Aitkin County)

Fact Sheet. Chesapeake Bay Water Quality

Life on the James Judging Water Quality Based on Macroinvertebrates

Today s Webinar: Types of Monitoring and Assessment Data and What They Mean

Water Quality and Macroinvertebrates By Teresa Matteson and Heath Keirstead Benton Soil & Water Conservation District

Science Enhanced Scope and Sequence Grade 6. Water Quality

Mr. Leach Science Burrillville High School

Effects of Agricultural Land Use on Water Quality at the Watershed Scale

Our Watershed. 5-mile Creek. Natural Features: Wetlands, small bodies of water, and Forested areas

Results from the 2017 Water Quality Monitoring Program

Pennsylvania Pequea and Mill Creek Watershed Section 319 National Monitoring Program Project

Urban Riparian & Stream Restoration Program: Management & Photo Monitoring. Texas Water Resource Institute

Appendix D: Visual aids and handouts for graphing lessons

Carp Creek 2013 Summary Report

Determination of Total Nitrogen and Phosphorus in Environmental Waters

Pennsylvania s TMDL Program

U.S. Department of the Interior U.S. Geological Survey


WATERSHED. Maitland Valley. Report Card 201

Riffle Beetles to Riparian Buffers

Which Data Are Important And Why? Barry Tonning Tetra Tech

Riparian Areas. 101 An overview. Prepared by: Jacque Sorensen, M.Sc. TRU Department of Natural Resource Sciences

Wood Canyon Emergent Wetland Project. City of Aliso Viejo 12 Journey, Suite 100 Aliso Viejo, CA 92656

«225 «146. ^_ Texas Stream Team. !. Monitoring Station. "/ USGS Flow Station # Wastewater Outfall. Location Map. Morgan's Point. La Porte.

Flathead-Stillwater TMDL Planning Area Sampling Project : Nutrients, Metals Sampling and Analysis Plan

CHAPTER 4 WATERSHED PLAN GOALS & OBJECTIVES

SENR Forestry, Fisheries & Wildlife 122 Hours - Autumn Semester 2016

Summary. River. 5 th 8 th. about the. Chemical. anteceden. Grade Level: 5 th. 12 th. Objectives: instructions to. determine the. Chicago River Field

beneficial management practices

Envirothon Aquatics. Mike Archer, NE Dept. of Environmental Quality. Katie Pekarek, Nebraska Extension Jeff Blaser, Nebraska Game and Parks

Freshwater Ecosystems

An Evaluation of Antes Creek. Antes Creek has a drainage area of square miles and is a tributary of the

Water Quality Assessment for the Town of Caswell Beach, 2008

Monitoring Stormwater Best Management Practices: Why Is It Important and What To Monitor

Stream Ecology. Physical Characteristics

WOW: WATERSHEDS BASELINE AUDIT, GRADES K-2 TABLE 1. GEOGRAPHIC INFORMATION

OCEANS AND AQUATIC ECOSYSTEMS- Vol. I - Geographic Information Systems Applied to the Analysis of Riparian Buffer Zones and Lakes - Norio Tanaka

Anthropogenic Impacts on Bays and Watersheds. HI-MOES Presentation 2009 The Kohala Center Kohala Watershed Partnership

Transcription:

Comparison of Total Phosphorus and Macro Invertebrates and the Impact of Land Use on Water Quality Laura Roldán Isardo Braverman Puerto Rico

The Streams Project The Streams Project is an effort by VT EPSCoR to collect data on streams. The recollected water quality data is placed in the VT EPSCoR database. These data are later combined with other stream s data in order to find strategic solutions to the pollution problems and gain a greater understanding of our watersheds.

Objectives Find the correlation of macro-invertebrates, phosphorus and total suspend solid in Maracuto Stream. Determine how land use affect the physical condition and water quality in streams. Identify possible sources of pollution affecting the water quality.

Maracuto Stream Downstream The Maracuto stream is located in Carolina, PR. This stream connects with the Río Grande de Loíza, one of the most important rivers in Puerto Rico, and supplies water for the SJMA. Two sites were chosen based on the areas surrounding the stream. Upstream

Hypothesis By determining the sources of pollution that may affect the water quality we can make recommendations for interventions to improve water quality. Urban development surrounding can alter the dynamic of the water flow, therefore may be causing damages to the macroinvertebrates habitat and the ecosystem in the stream. If phosphorus levels increase more amount of particles will be found in the water.

Materials The monitoring locations were identified using a GPS. Phosphorus, and TSS were taken using sterile sample containers. Samples were stored in a cooler during transportation and later frozen until analyzed. Phosphorus was tested using a spectrophotometer. For the TSS test a 0.45µm filter was used. Streams Project database, GIS and Google Earth program were used field for observations and aerial photo interpretation.

Methodology: Assessments General Stream Site Assessment - The immediate surrounding landscape and the physical characteristics of the stream reach. Detailed Habitat Assessment & Physiochemical Parameters - The biological condition of a stream system is determined through a visual assessment of in-stream and riparian habitat quality.

Methodology: Water samples Phosphorus Via a persulfate digestion followed by analysis for orthophosphate concentration using the ascorbic acid reduction method on a UV 1800 spectrophotometer. TSS A known volume of water is run through a 0.45µm filter. Solids collected on the filter cause a change in filter weight that is reported as total solids in mg/l.

Methodology: Macro invertebrates Four replicates were collected from each site by the hand-scrub method. The samples were store in a plastic bag with 100% ethanol for specimen preservation. Every insect was observed with a microscope to identify and classify the insects by family and specie with the Guide to Aquatic Invertebrates. They were separated and classified in laboratory by their physical characteristics.

Methodology: GIS Maps It is used to see the regional land use practices and determine possible sources of pollution that may be affecting the water quality. Such findings can be useful in the remediation of impaired watersheds, and in identifying unexamined watersheds with a high risk of impairment. Geology Hydrology Land Use Built Infrastructure

Results and Discussion: Assessments 80% Upstream (forest area) status indicate good water condition to support aquatic life 66% Downstream (urban area) status is partial support indicating not so good water conditions and possibly impaired water. Designated Use Designated Use Group Status Aquatic Life Fish, Shellfish, And Wildlife Protection And Propagation Impaired Primary Contact Recreation Recreation Good Public Water Supply Public Water Supply Impaired Secondary Contact Recreation Recreation Good US EPA 2006 overall water status

Results and Discussion: Water samples Phosphorus (µg/l) 600 500 400 300 200 100 Phosphorus analysis Downstream Upstream TSS (mg/l) 450 400 350 300 250 200 150 100 50 0 Total suspended solids analysis Day 1 Day 2 Day 3 Downstream Upstream 0 Day 1 Day 2 Day 3 Phosphorus is a commonly found in agricultural fertilizers, manure, and organic wastes in sewage and industrial effluent. TSS is not only an important measure of erosion in rivers; it is also closely linked to the transport through river systems of nutrients, especially phosphorus.

Results and Discussion: Macro invertebrates Total Count 140 120 100 80 60 40 20 0 Macro invertebrates found by site 117 Downstream Site 84 Upstream The overall abundance of macro-invertebrates appears to be related to nutrient levels. Because of the levels of phosphorus were more in the downstream (urban) area larger quantities of benthos were found.

Results and Discussion: Macro invertebrates Count 50 40 45 30 35 20 25 10 15 0 5 Macro invertebrates comparison Downstream Upstream Family Juvenile mayflies require abundant dissolved oxygen and are very sensitive to pollution. They are typically found in good quality streams, along with riffle beetles, caddisflies, and some species of snails.

Conclusions The quarry, urban development, runoff, organic wastes from septic tanks and the stable were identified as possible sources of pollution. If phosphorus levels increase, TSS and the quantity of benthos also increase. Conditions for water quality in upstream (rural) area were better than downstream (urban) area.

Conclusions We manage to find the total abundance, species richness and dominance in the stream. The Coleoptera family was the most abundant family in both sites. Larger amounts of macro-invertebrates were found in the urban area than the rural area. The levels of nutrients found on each site explain this.

Future Projects Include other parameters to evaluate water quality. Currently, 13,308 residences are located <100 meters from the channel of a water body in rural areas in PR. This residential areas can be a source of pollution because most of them use septic tanks, therefore, clearly having an impact on the stream.

University of Vermont Saint Michael's College VT EPSCoR Stream Project Declan McCabe, macro invertebrate specialist Lexie Reiss Haselton, GIS/ Database Specialist Dr. Juan F. Arratia, AGMUS Student Research Center at Universidad Metropolitana, San Juan, PR Yiria Muñiz, mentor José E. Aponte de la Torre School, Carolina, PR