Eutrophic Water

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Eutrophic Water

Lake Water Quality
-- phosphorus content
-- chlorophyll a content and
-- visibility through the water
Eutrophic:
In lake aging pertains to an old-age lake and indicates high supply of nutrients supporting high biologic productivity.
Ecology of a lake or other body of water, containing a rich supply of plant nutrients and characterized
by seasonal periods of oxygen deficiency as a result of excessive growth of algae. 
Eutrophic Pools - Two Possible States

The phosphorus content, chlorophyll a content and visibility through the water are used in the classification of lake water quality.

Mesotrophic lakes
are those normally associated with clear water conditions and a good diversity of plant and animal life.

Hypertrophic Lakes
have high phosphorus levels leading to algal blooms, coloured water and the loss of higher plants.

Pools found in urban areas are generally eutrophic
-- characterized by high nutrient levels, and a consequent lowering of species diversity. Restoring pools to a mesotrophic state may be very difficult.

Research indicates that eutrophic lakes may exist in one of two possible states:

they may either by
murky and green with high levels of algae;

or:

they can exist
as clear water with higher plants and a greater ecological diversity.

The depth of water, extent of surface area and type of construction (steep, shelving, etc.) have great bearing on any problems and their possible solutions.

Site: http://www.wildlifetrust.org.uk/urbanwt/ecorecord/bap/html/uponds.htm |


Eutrophic Water | Eutrophication
Site: http://www.dragonflyireland.fsnet.co.uk/lakes_3.htm |
Site: http://www.des.state.nh.us/factsheets/bb/bb-27.htm |
Site: http://www.dragonflyireland.fsnet.co.uk/ponds_b.htm |
Dictionary: http://www.bartleby.com/61/50/E0245000.html |
Site: http://www.pku.edu.cn/academic/xb/99/_99e414.html |
Site: http://www.spatial.maine.edu/~snoox/eutrophic_lakes.htm |
Site: http://www.ukbap.org.uk/ |
Site: http://www.wildlifetrust.org.uk/urbanwt/ecorecord/bap/html/uponds.htm |
Pond
Pond
Eutrophication.

Historically, aquatic systems have been classified as oligotrophic or eutrophic.

Oligotrophic waters
are poorly fed by the nutrients nitrogen and phosphorus and have low concentrations of these constituents. There is thus low production of organic matter by photosynthesis in such waters.

By contrast, eutrophic waters
are well supplied with nutrients and generally have high concentrations of nitrogen and phosphorus and, correspondingly, large concentrations of plankton owing to high biological productivity. The waters of such aquatic systems are usually murky, and lakes and coastal marine systems may be oxygen-depleted at depth.

The process of eutrophication
is defined as high biological productivity resulting from increased input of nutrients or organic matter into aquatic systems. For lakes, this increased biological productivity usually leads to decreased lake volume because of the accumulation of organic detritus. Natural eutrophication occurs as aquatic systems fill in with organic matter; it is distinct from cultural eutrophication, which is caused by human intervention. The latter is characteristic of aquatic systems that have been artificially enriched by excess nutrients and organic matter from sewage, agriculture, and industry.

Naturally eutrophic lakes
may produce 75-250 grams of carbon per square metre per year, whereas those lakes experiencing eutrophication because of human activities can support 75-750 grams per square metre per year.

Commonly, culturally eutrophic aquatic systems
may exhibit extremely low oxygen concentrations in bottom waters.

This is particularly true of stratified systems,
as, for instance, lakes during summer where concentrations of molecular oxygen may reach levels of less than about one milligram per litre -- a threshold for various biological and chemical processes.

Aquatic systems may change from oligotrophic to eutrophic,
or the rate of eutrophication of a natural eutrophic system may be accelerated by the addition of nutrients and organic matter due to human activities. The process of cultural eutrophication, however, can be reversed if the excess nutrient and organic matter supply is shut off. This response was demonstrated in the Great Lakes of the north central United States which have responded to government regulations of the early 1970s aimed at reducing phosphorus inputs (principally from detergents) into these lakes.

Not only do freshwater aquatic systems undergo cultural eutrophication,
but coastal marine systems also may be affected by this process. On a global scale, the input by rivers of organic matter to the oceans today is twice the input in pre human times, and the flux of nitrogen, together with that of phosphorus, has more than doubled. This excess loading of carbon, nitrogen, and phosphorus is leading to cultural eutrophication of marine systems.


Site: http://state-of-coast.noaa.gov/bulletins/html/eut_18/eut.html |
Site: http://state-of-coast.noaa.gov/bulletins/html/eut_18/national.html |

Site:

| http://www.shef.ac.uk/uni/academic/A-C/aps/level2modules/aps201/eutrophic.html |
Trophic state

Oligotrophic:
larger, deeper lakes with clear water, rocky or sandy shorelines, low phosphorus enrichment, limited rooted plant growth, low algal growth and adequate dissolved oxygen throughout.
Mesotrophic:
an intermediate category with characteristics between the other two groups.
Eutrophic:
smaller, shallower ponds with mucky bottoms, extensive rooted plant growth and depleted dissolved oxygen in the bottom waters; often tea-colored and sometimes murky from planktonic algal growth.
Site: http://www.des.state.nh.us/factsheets/bb/bb-27.htm |
Dissolved Oxygen

This criterion can be used only for lakes that are deep enough to develop a cold bottom layer of water (hypolimnion) during the summer. The extent of dissolved oxygen depletion in the hypolimnion is a measure of decomposing organic matter in the bottom waters and in the sediments, and represents an indirect measure of the biological production in the lake.


Dissolved Oxygen (mg/L) ------------------------------- Trophic Category
> throughout the lake --------------------------------------- oligotrophic
< 1 in less than half of the hypolimnion volume ------------ mesotrophic
< 1 in more than half of the hypolimnion volume ----------- eutrophic

Pond
Site: http://www.des.state.nh.us/factsheets/bb/bb-3.htm |
Trophic state

Lake Eutrophication

What is lake aging?

Lake aging is the natural process by which a lake fills in over geologic time with erosional materials carried in by the tributary streams, with materials deposited directly through the air, and with materials produced in the lake itself. From the time that a lake is created (by glacial action), the aging or filling in process begins. Although New Hampshire's lakes have the same chronological age, they age (i.e. fill in) at different rates because of differences in runoff and watershed characteristics. The natural succession is from lake to pond, pond to marsh, marsh to meadow, and meadow to dry land. Examples of each can be seen today including areas of dry land where past lake basins can still be identified.

What is eutrophication?

Eutrophication is the process of increased nutrient input to a lake over the natural supply. This increased lake fertilization usually results in an increase in the biological production that occurs in the lake. Although the increased production may increase the rate of lake filling, it is incorrect to define eutrophication as lake aging. A lake dies not when it reaches a high state of productivity, but when it no longer exists (i.e. is filled in). Lake filling results both from production that occurs in the lake, which may increase with eutrophication, and from organic and inorganic material deposited from outside the lake, which has no relationship with lake eutrophication.

What activities cause eutrophication?

Since eutrophication is increased nutrient input, any activity in the watershed of a lake that increases nutrient input causes eutrophication. Land use changes can result in significant changes in nutrient runoff. Studies in New Hampshire have shown that phosphorus export from agricultural lands is at least 5 times greater than from forested lands, and urban areas may be more than 10 times greater. Other activities that contribute to eutrophication are lawn and garden fertilizers, faulty septic systems, washing in or near the lake, erosion into the lake, dumping or burning leaves in or near a lake, and feeding ducks.

What is meant by trophic state?

The trophic state of a lake is a hybrid concept with no precise definition. Originally, trophic referred to nutrient status. Eutrophic water was water high in nutrients and, by extension, a eutrophic lake was a lake that contained eutrophic water. Later the concept of trophic state was applied to lakes rather than water, and its precise definition was lost. Now trophic state not only refers to the nutrient status of the water, but also to the biological production that occurs in the water and to the morphological characteristics of the lake basin itself. Now a eutrophic lake may not only be a lake with high levels of nutrients, but also a very shallow pond, full of rooted aquatic plants, that may or may not have high nutrient levels.

Lakes are divided into three trophic categories: oligotrophic, mesotrophic, and eutrophic. An oligotrophic lake is typically a large deep lake with crystal clear waters and a rocky or sandy shoreline. Both planktonic and rooted plant growth are sparse, and the lake can support a coldwater fishery. A eutrophic lake, on the other hand, is typically shallow with a soft, mucky bottom. Rooted plant growth is abundant along the shores and out into the lake, and algal blooms are not unusual. Water clarity is not good and the water often has a tea color. If deep enough to thermally stratify, the bottom waters are devoid of oxygen. Mesotrophic is an intermediate trophic state with characteristics between the other two.

Trophic state
Oligotrophic:

Steep Sided, Clear Water
Low Nutrient Enrichment
Little Planktonic Growth, Low Productivity
Few Aquatic Plants
Sand or Rock Along Most of Shoreline
Coldwater Fishery
High Dissolved Oxygen Content
Mesotrophic:
Moderate Nutrient Enrichment
Moderate Planktonic Growth
Some Sediment Accumulation Over Most of Lake Bottom
Usually Supports Warmwater Fish Species
Eutrophic:
High Nutrient Enrichment
Much Planktonic Growth (High Productivity)
Extensive Aquatic Plant Beds
Much Sediment Accumulation on Lake Bottom
Low Bottom Dissolved Oxygen
Only Warmwater Fish Species


Trophic state
Site: http://www.dnr.state.wi.us/org/water/fhp/lakes/under/trophics.htm |

Trophic state is another indicator of water quality.

Lakes can be divided into three categories based on trophic state
-- oligotrophic
-- mesotrophic, and
-- eutrophic.

These categories reflect a lake's nutrient and clarity levels.


Oligotrophic lakes
are generally clear, deep and free of weeds or large algae blooms.
Though beautiful, they are low in nutrients and do not support large fish populations.
However, oligotrophic lakes often develop a food chain capable of sustaining a very desirable fishery of large game fish.

Mesotrophic lakes
lie between the oligotrophic and eutrophic stages.
Devoid of oxygen in late summer,
their hypolimnions limit cold water fish and cause phosphorus cycling from sediments.

Eutrophic lakes
are high in nutrients and support a large biomass
(all the plants and animals living in a lake).
They are usually either weedy or subject to frequent algae blooms, or both.
Eutrophic lakes often support large fish populations,
but are also susceptible to oxygen depletion.
Small, shallow, eutrophic lakes are especially vulnerable to winterkill
which can reduce the number and variety of fish.
Rough fish are commonly found in eutrophic lakes.



A natural aging process occurs in all lakes, causing them to change from oligotrophic to eutrophic over time, and eventually to fill in (Figure 3). People can accelerate the eutrophication process by allowing nutrients from agriculture, lawn fertilizers, streets, septic systems, and urban storm drains to enter lakes.

In nutrient-poor areas, the aging process may lead instead to dystrophic and bog lakes which are highly colored, acid, and not as productive as eutrophic lakes.

Researchers use various methods to calculate the trophic state of lakes.

Common characteristics used to make the determination are:


total phosphorus concentration (important for algae growth)

chlorophyll a concentration (a measure of the amount of algae present)

Secchi disc readings (an indicator of water clarity)


The Trophic States
associated with these three measures are shown below:
Clearly, low levels of phosphorus are associated with low levels of algae (chlorophyll a),
which are associated with high Secchi disc readings.

Trophic class -----  Total phosphorus ug/l ------ Chlorophyll a ug/l --------- Secchi Disc feet

Oligotrophic ----------------  3 --------------------------- 2 -----------------------  12
-------------------------------10 -------------------------- 5 ------------------------   8
Mesotrophic ----------------- 18 -------------------------- 8 ------------------------   6
------------------------------- 27 ------------------------- 10 ------------------------   6
Eutrophic -------------------- 30 ------------------------- 11 ------------------------   5
-------------------------------  50 ------------------------- 15 ------------------------   4
Secchi Disc
Measuring Turbidity

Background

What do plants need for growth? One answer is light. Because underwater plants need light too, and they die if they can't get enough, water clarity is an important factor in wetland habitats. Fewer plants means less food for many animals, and less production of oxygen from plants to help keep the water environment healthy. Young and otherwise vulnerable creatures find protection in beds of underwater plants. These plants also feed and protect many of the foods we eat, including fish, crabs, ducks, and geese.

When water is cloudy, it is said to be turbid.
Turbidity is caused when sediment (soil and other particles that settle to the bottom) and other materials are stirred up in the water. When loose soil from construction sites, bare lawns, and eroding shorelines washes into a wetland, sediment levels rise.

Excess nutrients in runoff promote the growth of algae, which also clouds the water. Rain, wind, waves, tides, animals, and various human activities can all stir up these suspended solids and increase turbidity.

Turbidity blocks the sunlight that is so vital to aquatic life. Fish, oysters, and other gilled creatures suffocate when their gills are clogged by sediment. Suspended particles absorb heat from sunlight as well, warming the water and decreasing DO.

A Secchi (SECK-key) disk
is used to measure depth of light penetration, or turbidity.

The deeper the disk is visible, the clearer and less turbid the water.

Secchi disks are used in water that is fairly deep and slow or still. For shallow wetlands a turbidity test kit can be used.

If the secchi disk disappears at less than 12 inches
— muddy water or high algae content that could effect plant growth or deplete oxygen.

If secchi disk disappears at 18-24 inches
— sufficient for most plant growth and animal growth.

Procedure

1. List as many sources of sediment as you can.
Try to use specific examples -- things you have seen in the area or at home.

2. If the water in your wetland is deep enough and slow-moving or still,
construct Secchi discs as follows:


a. Paint the tin can lid white, then paint a large black X on top.

b. Punch or drill a small hole in the middle of the X
and attach the string to the lid with the eye bolt and nut.

c.Mark off 0.5-meter (or 1-foot) increments on the string with the marker


3. At the wetland, gently lower the disc straight down into the water
until you can no longer see the X.

Then, inch the disc back up until you can just barely see the X and hold the disc there.

Reach down and grasp the string right at the surface of the water,
and hold the string there while you pull the disk back out.

Read the marking on the string to determine the depth to which light could penetrate.
Compare readings from several places in the wetland.

1. Were some places more turbid than others?

2. Were you able to see what caused the turbidity? Hint: Look for places where runoff and sediment are washing into the water from land.

3. Are fish stirring up the water?

4. Are you standing in the water?


Note: If the water in your wetland is shallow or fast-moving, you may skip this part or use a turbidimeter or turbidity test kit, if there is one available to you. Most turbidity test kits measure turbidity in turbidity units. Two (2) turbidity units indicates clear water (relatively free of sediments). Over 200 turbidity units indicates algae rich water or water with enough suspended solids to possibly effect plant growth. You could also use clear 1 liter jars to collect running water at different places, let the jars sit until the solids settle out, and compare solids collected at the different sites by weight or volume. Suspended solids measuring 250-500 milligrams per liter (mg/l) can effect food production and reproduction.
Turbidity Test Kit
for shallow wetlands -- Forestry Suppliers 1-800-647-5368

Eutrophic Water
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