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Aquatic Pest

Control









Kansas State University Agricultural Experiment Station

and Cooperative Extension Service





Category 5

Table of Contents

Introduction

Purpose and Content ....................................................................... 3

Standards of Competency ................................................................ 4



Aquatic Vegetation

Impounded Waters ......................................................................... 5

Flowing Waters ............................................................................... 5

Water Saturated Areas ..................................................................... 5

Classification of Aquatic Plants ....................................................... 6

Aquatic Invasive Plants ................................................................... 9

Control .......................................................................................... 11

Herbicide Use

Improper Use ................................................................................. 15

Proper Use ..................................................................................... 16

Herbicides for Aquatic Use ........................................................... 18



Nusiance Animal Control

Invertebrates .................................................................................. 24

Fish ................................................................................................ 25

Amphibians .................................................................................. 26

Reptiles .......................................................................................... 27

Birds .............................................................................................. 27

Mammals ....................................................................................... 27



Parasites and Diseases of Fish

Approved Drugs ............................................................................ 29



Calculations

Area ............................................................................................... 32

Volume .......................................................................................... 32

Flow .............................................................................................. 32

Additional Information

References ..................................................................................... 36



Directions for Using this Manual

This is a self-teaching manual. At the end of each major section is a list

of study questions to check your understanding of the subject matter.

These study questions are representative of the type that are on the

certification exam. By studying this manual and answering the study

questions, you should be able to gain sufficient knowledge to pass the

Kansas Commercial Applicators Certification examination. Correct

2

answers appear on page 37.

Introduction

Purpose and Content

The purpose of this training

Numerous demands are placed on

manual is to provide practical

the state’s aquatic resources. Water

information on aquatic pest control

is used in various ways. Each use

in accordance with standards of

requires a certain quality and

competency provisions in the

condition.

Federal Insecticide, Fungicide, and

Sometimes a particular water Rodenticide Act.

use alters quality and condition,

This manual contains information

so other uses are impaired.

for several aquatic pests and their

Often, water contains a problem

control:

organism that must be eliminated

or controlled to make it suitable • Aquatic vegetation

for a particular use. The desired • Nuisance animals

control method must be effective, (invertebrates and vertebrates)

economical, and above all, safe

for the applicator, nontarget • Parasites and diseases of fish

organisms, and the environment. Major emphasis is on use of

Chemical control often is a choice pesticides for control, but

among available pest control alternative methods are usually

methods. This manual primarily considered. Although this

addresses methods employing publication provides a basic

pesticide applications, but operating framework, it does not

mentions alternatives. contain information necessary for

Manufacture and use of identification and control of all

pesticides for aquatic pests is aquatic pests. Study the suggested

minor compared with other references at the end of the manual

chemical uses. Companies seldom for more information.

invest resources to develop

research data required by the

Environmental Protection Agency

to be considered for registration

of a pesticide for aquatic use.

A relatively small number of

pesticides can legally be used

in the aquatic environment,

but many pesticides available

for the terrestrial environment

effectively kill aquatic pests. This

has led aquatic workers to use any

pesticide that will work and often

results in destruction of nontarget

organisms and residue levels in

fish flesh and sediments. Activities

like these are illegal and leave the

applicator liable to both criminal

and civil penalties.

3

Introduction

Standards of application of restricted

use pesticides used in

Competency this category. They shall

The Environmental Protection demonstrate practical

Agency in CFR 171.4, “Standards knowledge of various water

for Certification of Commercial use situations and the

Applicators,” states: potential of downstream

Commercial applicators effects. Further, they must

in each category shall be have practical knowledge

particularly qualified with concerning potential

respect to the practical pesticide effects on plants,

knowledge standard fish, birds, beneficial insects,

elaborated below: and other organisms that

may be present in aquatic

Applicators shall demonstrate environments. Applicators

practical knowledge of the shall demonstrate practical

secondary effects, which knowledge of the principles

can be caused by improper of limited-area application.

application rates, incorrect

formulations, and faulty









4

Aquatic Vegetation

caused by the decaying vegetation.

This can occur at almost any time

Plants have adapted to thrive of year, but is most common in

in diverse habitats. They are midsummer and in mid winter

most obvious in the terrestrial during ice cover.

environment, but they also can Summer kills usually occur after

inhabit many types of aquatic periods of hot, calm, cloudy

environments. Aquatic plants weather. During these times plants

are more numerous in the warm, greatly reduce photosynthesis,

swampy areas of the southern but continue to respire and often

United States, but numerous die and decompose. Winterkills

examples can be found in Kansas. occur during periods of ice and

Aquatic plants are a natural part snow cover. Ice usually allows

of the aquatic ecosystem, used by enough light penetration for

many animals as food or a hiding photosynthesis, but a layer of snow

place. Many people find aquatic can block out most light. This

plants interesting and attractive. light blockage prevents oxygen

As with all naturally occurring production, but respiration and

organisms, they may interfere decomposition continue, resulting

with people’s activities because in an oxygen shortage.

of their overabundance or mere

presence. When this occurs, the Flowing Water (Rivers,

plants are considered “weeds,” and Streams, and Canals)

some control is desired. Different

problems occur in different types Aquatic vegetation is seldom a

of waters. The main water types problem in the rivers and streams

and associated aquatic plant of Kansas. In fact, vegetation along

problems are as follows: the banks is beneficial because it

protects the banks from erosion.

Impounded Waters Problems can occur in canals,

which are designed to transport

(Ponds, Lakes, and water. Plants growing along the

Reservoirs) edge, especially trees, can impede

The most common aquatic water flow.

vegetation problems occur in

impounded waters. Abundant Water Saturated Areas

vegetation affects fish populations (Marshes, Seeps, and

in these bodies of water. Small fish Drainage Ditches)

hide in the vegetation, making

them unavailable to predators. This Aquatic plants usually are not

often results in overpopulation a major problem in these areas.

and stunting of certain species. Encroaching vegetation may

Excessive vegetation interferes impede flow in drainage ditches.

with fishing, swimming, and Marshes and seep areas usually

boating, and dead, decaying cannot be used for conventional

vegetation produces offensive Kansas agriculture so the

odors. A more serious problem vegetation can be left alone for

results from the oxygen deficiency

5

Aquatic Vegetation

wildlife habitat. Weed problems crushed, chara produces a musky

can occur in cultivated fields that odor.

border these wet areas, especially

in abnormally wet years. During Floating Plants

these times, the aquatic plants Some plants are free-floating

invade fields and cause special while others, rooted in the bottom,

weed-control problems. have floating leaves that rise or fall

with the water level. Many floating

Classification plants grow rapidly and are among

the most troublesome aquatic

of Aquatic Plants plants. Duckweeds (Lemna spp.)

Problem weed species must be and watermeal (Wolffia spp.) are

identified before an appropriate true floating plants of this group

weed-control practice can be whose roots feed from water rather

selected. Aquatic plants are than soil. Rooted plants with

classified by a similar growth floating leaves include waterlilies

habit as: algae, floating plants, (Nymphaea spp.) and American

submersed plants, emersed plants, lotus (Nelumbo spp.). Many lotus

and marginal plants. leaves float, but some extend above

the surface.

Algae

There are three major forms of

freshwater algae: phytoplankton

(planktonic), filamentous, and

chara. Planktonic algae are usually

beneficial unless water is used for

human consumption. Planktonic

and filamentous algae may clog

filters in water treatment plants

or produce undesirable tastes

and odors in drinking water.

Filamentous algae interfere with

irrigation systems by clinging to

structures and concrete linings Duckweed

and clogging weirs and screens.

Common filamentous algae

are Spirogyra spp. — slimy and

green; Cladaphora spp. — cotton

mat type; and Pithophora spp.

— horsehair clump type. Nitella

spp. and Chara spp. (also called

muskgrass) are large green algae

that are anchored to the bottom

but do not extend above the

surface. Stem-like, with thin,

leaf-like structures, they are often

confused with seed plants. When

Watermeal

6

Aquatic Vegetation

Submersed Plants

Submersed plants are true seed

plants with roots, stems, and leaves.

Rooted on the bottom, these plants

grow chiefly below the surface,

although their flowers and seeds

and a few leaves may extend above

it. A depth of 10 to 12 feet in clear

water is the limited habitat for

most submersed plants. Important

submersed plants include:

pondweeds (Potamogeton spp.),

elodea (Elodea spp.), watermilfoil

(Myriophyllum spp.), coontail Naiad

(Ceratophyllum spp.), naiads (Najas

spp.), hydrilla (Hydrilla verticillata) Emersed Plants

and bladderwort (Utricularia spp.). Emersed plants are rooted in the

bottom and produce most of their

leaves and flowers at or above the

surface. Leaf shape, size, and point

of attachment are variable within

this group. Leaves of emersed

plants do not rise and fall with the

water level as do those of attached

floating plants. Important emersed

plants include: watershield

(Brasenia spp.), arrowhead

(Sagittaria spp.), water primrose

(Ludwigia spp.), and waterwillow

(Justicia spp.).



Pondweed









Arrowhead



Coontail





7

Aquatic Vegetation









Water Primrose Smartweed



Marginal Plants Identification

Marginal plants are emersed plants Target weeds in the water-use

that grow on saturated soil beyond area must be correctly identified

the water’s edge. These plants so appropriate control practices

vary in size, shape, and habitat. can be selected and applied. For

They may be found growing identification of unfamiliar aquatic

in moist soils along shorelines plants, take samples of entire

into water up to 2 feet in depth. plants (roots, stems, leaves and

Important marginal weeds are flowers if available) to your local

reeds (Phragmites spp.), sedge K-State Research and Extension

(Carex spp.), bulrush (Scirpus spp.), agent. If necessary, the agent can

rush (Juncus spp.), cattails (Typha send the aquatic plants to the

spp.), giant cutgrass (Zizaniopsis Herbarium, Division of Biology,

spp.), smartweeds (Polygonum for proper identification. Control

spp.), purple loosestrife (Lythrum information can be requested if

spp.), willow (Salix spp.), saltcedar you desire management practices

or tamarisk (Tamarix spp.) and for the aquatic plants based on the

cottonwood (Populus spp.). plant identification report.









Bulrush



8

Aquatic Vegetation

Aquatic Invasive Plants

Kansas has five invasive plant

species that individuals should be

aware of in aquatic environments.

These plants pose a threat to

the health of Kansas aquatic

ecosystems and on the human

use of those resources. In order

to help prevent their spread, it is

important to be aware of these

plant species and their identifiable

features.

Hydrilla

Hydrilla

Hydrilla (Hydrilla verticillata)

has leaves that are small, pointed

and arranged in whorls of four to

eight along the stem. This plant

is submersed with long, slender

branches that branch and spread

across the water. The leaf margins

are distinctly saw-toothed making

it rough to the touch. Hydrilla

limits recreational activities

because it forms a thick mat that

Eurasian Watermilfoil interferes with boating, swimming,

Eurasian Watermilfoil and fishing. It also slows the flow

Eurasian watermilfoil of water and clogs irrigation and

(Myriophyllum spicatum) is flood-control canals. Hydrilla

identified by the whorl arrangement spreads to new waters as fragments

of its three to five feather-like on boats and trailers, so it is

leaves. Each leaf contains 12 to 21 important to clean equipment.

pair of leaflets. The stems branch

near the water surface and it is

most commonly found in waters

less than 20 feet deep. Eurasian

watermilfoil forms dense mats on

the water surface, which competes

with native aquatic vegetation

and hinders recreational activities.

Milfoil spreads when plant pieces

break off and are carried by water

currents, boats, trailers, and fishing

gear to new locations. Early

detection of current populations

may help to prevent its spread.



9

Aquatic Vegetation

Saltcedar

Saltcedar (Tamarix spp.),

sometimes called tamarisk, is a

small tree or shrub that can reach

15 to 20 feet with red/brown

stems. This plant produces pink

flowers in May through October.

Saltcedar forms a monoculture

and dramatically affects vegetation

structure and animal diversity. It

can use up to 200 gallons of water

a day, thus has a negative impact

on the water flow. The plant also

Purple Loosestrife

accumulates salt in its tissues,

Purple Loosestrife which is later released in the soil,

Purple loosestrife (Lythrum creating an environment where

salicaria) is a perennial herb that other plants cannot grow. Saltcedar

can grow four to 10 feet high. is extremely difficult to eradicate

During the summer, the plant because it resprouts after being cut

produces a showy magenta- or burned.

colored flower spike. The leaves

are lance-shaped with a rounded

or heart-shaped base. Loosestrife

can produce over a million seeds,

which can be moved by water,

vehicles, and wildlife. This plant

restricts other native wetland

species and reduces habitat for

waterfowl. Small infestations may

be pulled by hand, but old plants

will need to be spot treated with a

herbicide.



Curly-Leaf Pondweed

Curly-Leaf Pondweed

Curly-leaf pondweed (Potamogeton

crispus) is a fast-growing perennial

that has simple, long, narrow

leaves. The flattened stems are

one to three inches long and 1/8

inch wide. In the spring, it forms

dense mats which interfere with

recreational activities and limit

the growth of native species.

Mechanical, biological and

Saltcedar chemical control techniques can be

effective.

10

Aquatic Vegetation

Control control cattails, willows, and

cottonwood trees in small ponds.

Control of aquatic weeds can Small amounts of submersed

be subdivided into four general plants can be pulled out or raked

categories: (1) prevention, (2) by hand. Larger amounts can be

mechanical and physical, (3) removed by pulling a long chain or

biological, and (4) herbicides. cable across a pond between two

Often a combination of these tractors.

practices is necessary for adequate

control. A device that is effective on

submersed vegetation is a

Prevention hand-pulled cutter, consisting

Effective planning and aquatic of a v-shaped flat metal piece

system management often sharpened on the outer edge. A

eliminates, or greatly reduces, rod is fastened to the point and a

the need for costly and time- rope attached to this. The device is

consuming weed-control practices. thrown out into the vegetation and

Aquatic weed problems typically pulled in with a jerking motion.

occur in clear, shallow water that This cuts off the vegetation so it

is high in nutrients. Ponds or lakes can float to shore where it can be

should be constructed so that raked out.

shallow water areas are minimized Submersed vegetation can also

by shaping the sides with a 3-to-1 be controlled by shading it with

slope (3 feet horizontal to 1 foot fine meshed dark plastic screen

vertical drop) down to a depth of similar to the type used to shade

at least 3 feet. Existing ponds or greenhouses. A large section of

lakes that have extensive shallow this material is placed over the

water areas can be dredged deeper, vegetation and weighted down

but a less expensive practice is to with rocks. This compresses and

use a bulldozer to deepen shallow shades the vegetation so it dies.

areas after the water level has After about 2 weeks, the screen

receded below these areas. can be moved to another area. The

Excessive nutrients should be advantage of this method is that

prevented from getting into the fishing, swimming, and boating

water since they will stimulate can take place over the screen.

rapid plant growth. Common Various types of weed harvesters

sources of nutrients are runoff have been used, including a cutting

from livestock holding areas, device on a floating barge. As the

septic tank drainage, and heavily weeds are cut, they are brought up

fertilized fields. on a conveyor and deposited on

the barge. Devices such as these

Mechanical and Physical

are expensive and disposal of the

Mechanical and physical control

wet, heavy plant material is a

methods will be more effective

problem.

in smaller bodies of water than

in larger bodies of water. Pulling All mechanical and physical

marginal plants by hand is an control methods are labor intensive

effective reduction practice to and give only short-term relief.

11

Aquatic Vegetation

They work best on small bodies of to 10 fish per acre are sufficient.

water that can be observed closely Control is achieved within one

so control can take place before year at these stocking levels. At

the problem gets too large. These half these levels, control may take

methods are especially effective in up to two years.

home sewage lagoons. For more

Stocking new, clear ponds and

effective control, use mechanical

lakes at three to five grass carp

and physical control practices in

per acre can prevent development

conjunction with biological or

of aquatic weed problems. Grass

chemical control methods.

carp need to be at least 10 to 12

Biological inches long to avoid predation

Herbivorous fish, the grass if predatory fish such as bass are

carp, sometimes called the white in the pond or lake. The initial

amur (Ctenopharyngodon idella), stocking should be effective for at

is an effective biological method least several years since these are

to control aquatic vegetation. A long-lived fish. A few replacement

member of the minnow family, fish can be stocked if aquatic weed

this fish is native to large rivers infestation increases.

of China and Siberia. It will not Only a few problems are associated

reproduce in ponds and lakes since with grass carp. They do not

it needs large, fast-flowing rivers reproduce in standing water

for reproduction. nor do they seem to compete or

The young grass carp feed on interfere with the game fish. They

small crustaceans and insects, may, however, cause some loss of

but as they grow larger, they clarity of the water. Clear weedy

shift their diet almost completely ponds become less clear when

to plant material. They prefer stocked with grass carp. As the

some plants over others, but will grass carp eat the vegetation, the

consume many species of floating nutrients are excreted through

and submerged plants found in wastes. These in turn stimulate the

Kansas. They will pull out and eat production of planktonic algae,

some of the emersed plants, but which decrease the clarity. Grass

will not be able to control them. carp are indiscriminate feeders and

They have voracious appetites and can get so large that they consume

grow rapidly until the plants are most of the desirable vegetation

controlled and then their growth in a pond and greatly reduce fish

levels off. productivity.



The amount of grass carp Grass carp are highly mobile and

needed for control of submersed they will readily leave a pond or

vegetation depends on the lake during periods of heavy flow

infestation of aquatic plants. Grass over the spillway. Use of mesh

carp at the rate of 20 fish per fence across the spillway can

acre are needed if at least half of prevent loss of these fish. Some

the area is normally covered by states have restrictions regarding

vegetation. For vegetation in only the use of grass carp, but Kansas

a narrow belt around the edge, five only requires that they be of

nonreproductive triploid genetics.

12

Aquatic Vegetation

Fertilizers added to water have large number of waterfowl needed

been used to control aquatic for control of submersed and

weeds. Fertilizers stimulate the marginal plants results in a large

growth of planktonic algae, amount of wastes, which fertilizes

which in turn decreases the water the water. This often results in

clarity, and prevents growth of algae problems.

submersed vegetation. Although

Barley straw has been used

it appears to be a good practice,

by researchers in the United

it usually creates other problems.

Kingdom to control a variety of

Additional nutrients may cause

planktonic and filamentous algae.

an increase of marginal vegetation

Results in the United States are

and also filamentous algae.

not consistent, but show that

Increased infestation of algae

the decomposing straw must be

and other vegetation may cause

subjected to well-oxygenated water

oxygen depletion as the plants

for it to become anti-algal. The best

die and decay. Fertilization is not

control is obtained by suspending

recommended in Kansas because

barley straw bales that have been

most waters in Kansas lakes and

broken apart and suspended in

ponds contain sufficient nutrients.

cages near the water surface. Use

Waterfowl have also been used about 100 to 300 pounds of straw

to control aquatic plants. Ducks, per acre but be aware that most

geese, and swans will eat aquatic waters in the Midwest are typically

vegetation. Many pond and lake stagnant and oxygen-poor.

owners enjoy waterfowl. But the









13

Introduction

Aquatic Vegetation Study Questions 5. Important marginal plants

include:

These study questions are to aid

you in learning the material on a. duckweeds and watermeal.

pages 3 through 13. b. coontail and bladderwort.

1. Use of terrestrial registered c. arrowhead and waterwillow.

pesticides in an aquatic control d. willow and smartweeds.

program can result in:

6. Control of aquatic weeds can be

a. destruction of nontarget done by:

organisms.

a. preventative methods.

b. residues in fish.

b. biological methods.

c. residues in the sediments.

c. mechanical and chemical

d. all of the above. methods.

2. Aquatic plants are: d. all of the above.

a. a natural part of the aquatic 7. For vegetation in a narrow belt

environment. around the edge of a lake, grass

b. seldom a problem in farm carp fish should be stocked at the

ponds. rate of ___ per acre.

c. used by aquatic animals for a. 1 to 3

food and hiding. b. 5 to 10

d. a and c are correct. c. 12 to 17

3. In Kansas, aquatic vegetation in d. 19 to 22

flowing water is seldom a problem

8. Aquatic weed control may vary as

in:

influenced by:

a. canals used for transporting

a. susceptibility of the weeds to

water.

herbicide.

b. rivers and streams.

b. weed stage of growth.

c. stock watering tanks.

c. rate and time of application.

d. farm ponds.

d. all of the above.

4. There are ___ major forms of fresh

water algae.

a. 1

b. 2

c. 3

d. 4









14

Herbicide Use

Improper Use

Herbicides may be used to control Improper Application Rates

aquatic weeds, but control may Proper use of herbicides requires

vary because of such factors as accurate application so water,

susceptibility of the aquatic weeds vegetation, or soil in an aquatic

to the herbicide, stage of growth, area is covered uniformly at the

rate of application, and the time rate recommended on the product

of application. Some herbicides label. Properly functioning,

also may cause injury to fish if not accurately calibrated equipment is

applied properly. This publication essential.

provides information on alternative Application of a herbicide below

herbicides and their use for aquatic the rate recommended on the

weed control. label can result in unsatisfactory

Herbicides are frequently the control of target aquatic weeds.

preferred method for control Herbicide application at a rate

of aquatic weeds in situations higher than the recommended

requiring fast results and control rate for the product is illegal and

for several months. But even can result in greater residue and/

chemical methods frequently or toxicity. Herbicides applied at

must be combined with hand or rates exceeding the recommended

mechanical weeding to remove rate can create a hazard by

remaining weeds and to prevent contaminating water used for

future spread by seed or other drinking, fish, livestock, other

plant parts. nontarget organisms, irrigation, or

other purposes.

Additional information on proper

use of registered herbicides for Incorrect Formulation

most effective aquatic pest control The use of an incorrect

and least or no effect on nontarget formulation can result in:

organisms or the environment can 1. Use of a product that is not

be obtained from the following effective or safe.

sources: information from

2. Increased toxicity resulting

product labels and manufacturers

in death or injury to fish and

of herbicides registered by the

other nontarget organisms.

Environmental Protection Agency

(EPA) for use in aquatic areas, 3. Increased hazard to humans

K-State Research and Extension, during application.

and Kansas Department of 4. Increased hazard of injury to

Wildlife and Parks. desirable nontarget plants.









15

Herbicide Use

Faulty Application not injure fish at concentrations

Faulty application can be the result required for weed control.

of the following:

Proper use of herbicides will result

1. Improperly calibrated in the most effective control of

equipment. aquatic weeds and little or no effect

2. Use of improper herbicide. on nontarget organisms or the

environment. Follow these rules:

3. Use of improper rate of

1. Select the appropriate

recommended formulation.

herbicide to control the

4. Application at improper stage of identified target weeds. Refer

plant growth of target weeds. to Table 1 for weed response

5. Application of foliar-applied to selected aquatic herbicides.

herbicides when weeds are 2. Consult with Kansas

not growing rapidly due to Department of Wildlife and

unfavorable growing conditions. Parks or the U.S. Fish and

6. Application to plants, water, Wildlife Service for advice

or areas not registered for if a proposed herbicide

treatment on product label. application might endanger

wildlife, fish, or their habitat.

7. Application during windy

or other undesirable weather 3. Apply the herbicide in

conditions. accordance with all directions,

warnings, and precautions on

8. Improper determination of the label. Refer to the Table

volume of lake or pond to be on page 18 for use restrictions

treated. of water treated with aquatic

9. Failure to take into account that herbicides.

overflow from a pond or lake is 4. Store excess pesticides under

flowing water. lock and key — out of reach

10. Failure to determine of children and animals —

downstream use patterns. and away from food and feed.

5. Properly dispose of empty

Proper Use pesticide containers.

All chemicals used for aquatic This manual contains pesticide

pest control should be applied in recommendations that are subject

accordance with the directions to change at any time. These

on the manufacturer’s label, as recommendations are provided as

registered under the Federal a guide. It is always the pesticide

Insecticide, Fungicide and applicator’s responsibility, by law,

Rodenticide Act. to read and follow all current label

Most herbicides have a low acute directions for the specific pesticide

oral toxicity, but a few aquatic being used.

herbicides are poisonous to human Due to constantly changing labels

beings, livestock, and other non- and product registration, some

target organisms. Some herbicides of the recommendations given in

are toxic to fish, but most do

16

Herbicide Use

this publication may no longer must be disregarded. No

be legal by the time you read endorsement is intended for

them. If any information in these products mentioned, nor is

recommendations disagrees with criticism meant for products not

the label, the recommendation mentioned.









Table 1. Response of Aquatic Weeds to Selected Herbicides1 and Approximate Treatment Costs

Aquatic Herbicide (Trade name)

Endothall

Copper Diquat Fluridone Glyphosate

(Aquathol

Aquatic Weed Aquatic Algaecides 2,4-D (Reward & and (Sonar and (Rodeo and Imazapyr Triclopyr

Classification Weed (Several) (Several) WeedtrineD) Hydrothol) Avast) Others) (Habitat) (Renovate)

Algae Chara E P G G2 P P P P

Filamentous E P G G2 P P P P

Planktonic E P P P P P P P

Floating

Plants Duckweed P G G P E3 F G P

Watermeal P P F P G3 F P

Rooted

Floating

Plants Waterlillies P E P P E E E E

Submersed Bladderwort P F E P E P P P

Plants Coontail P G E E E P P P

Elodea P E F2 E P P P

Naiad P F E E E P P P

Pondweeds P P G E E P P P

Watermilfoil P G G G E P P E

Emersed

Plants Arrowhead P E G P P E E

Water

Primrose P E F P F E G E

Marginal Cattails P F G P F E E F

Plants Smartweeds P F P P P E E E

Purple

Loosestrife P F P P P E E G

Willow P E P P P E E E

Cottonwood P G P P P G G E

$2.50-20/ $7-65/ $250-700/ $50-220/ $60-150/ $15-30/ $33-133/ $80-320/

Approximate Cost4 Acre-ft Acre-ft Surface acre Acre-ft Acre-ft Surface acre Surface acre Surface acre

1

E = Excellent, G = Good, F = Fair, and P = Poor or none. Refer to product labels for specific recommendations.

2

Hydrothol formulation only.

3

AS formulation only.

4

Herbicide cost varies with application rate, water depth, formulation, geography, and market fluctuations. Contact local supplier for current retail

prices.









17

Herbicide Use

Herbicides Rate of application: Rates for

algae control range from 0.67 to

for Aquatic Use 5.32 pounds of copper sulfate per

acre–foot of water. Four pounds

Copper Algaecides of powder or crystals per acre–

foot is generally strong enough

Copper Sulfate

to kill algae and stonewort in

Products and manufacturers:

most waters. This concentration

Copper Sulfate — Chem One

kills snails, but does not kill

Corp and Phelps Dodge.

fish. In alkaline water, stronger

Copper Sulfate use information: concentrations may be necessary.

Do not exceed 4 ppm in potable Treatment is ineffective in waters

water. Copper sulfate controls with total alkalinity greater than

microscopic algae, single-filament 250 ppm. In moderate to high

algae, and Chara (stonewort), alkalinity waters (greater than

but is not effective against 200 ppm), the copper chelated

submersed or emersed leafy weeds. products are recommended. Use

Copper sulfate may be used in only 1.2 pounds of copper sulfate

recommended concentrations per acre–foot in very soft water as

without harm in waters for fish may be killed at the 4-pound

livestock and irrigation. Copper rate.

sulfate corrodes galvanized cans

How to apply: Copper sulfate

and most spraying equipment.

is available in different crystal

Plastic sprinkling cans are

and granular grades depending

convenient for applying copper

on application needs. Crystals

sulfate.

may be scattered by hand on the

surface of small ponds or placed

Table 2. Water Use Restrictions with Aquatic Herbicides

Human

Aquatic Livestock

Fish Agricultural

Herbicide Drinking Swimming Consumption Dairy Meat Irrigation Spray

---------------------------------------(Number of days after treatment before use1)-----------------------------------

Copper Sulfate 02 0 0 0 0 0 0

Copper Chelate 02 0 0 0 0 0 0

2,4-D ---------------------------------------(Varies with formulation, consult the label)-----------------------------------

Diquat 3-5 0 0 1-5 1-5 5 5

Endothall 7-25 1 3 7-25 0 7-25

Fluridone X3 0 0 0 2-30 30

Glyphosate 2 0 0 0 0 0 0

Imazapyr 2 0 0 0 0 120

Tricolpyr X4 0 0 0 0 120 120

Aquatic Dyes X 0 0 0 0 0 0



Always consult product labels for current restrictions.

1

X = Do not use treated water for that purpose.

2

Elemental copper concentration should not exceed 1.0 ppm if water is used for drinking.

3

Do not apply within 0.25 mile of any functioning potable water intake.

4

Refer to label.





18

Herbicide Use

in a burlap bag and towed behind be toxic to trout and other species

a boat. Crystals or powder can be of fish in soft water (<50 ppm

dissolved in water and applied by carbonate hardness).

spraying the water surface. If a

heavy growth of algae is present, 2,4-D

treat only one-third or one-half

of the pond at a time at weekly 2,4-D Low Volatile Ester

intervals. This prevents depleting Granules

the oxygen when the mass of Products and manufacturers:

dead organic matter decomposes. Aqua-Kleen — Cerexagri;

You may treat an isolated mass of Navigate — Applied Biochemists,

stonewort or algae without treating Inc.

the whole pond.

Herbicide use Information: For

Caution: Residual copper is toxic use to control specified aquatic

to many aquatic animals. Frequent weeds (refer to product labels) in

and continued use may result in ponds and lakes. Granules sink to

the kill of a large part of the fish- bottom and release weed-killing

food supply. chemical in the critical root zone

area. Apply 100 to 200 pounds

Copper Chelates

per acre by portable spreader or

Products and manufacturer:

mechanical spreader. During

Cutrine-Plus and Stocktrine II —

growth season, weeds decompose

Applied Biochemists, Inc., K-Tea

in a 2- to 3-week period following

and Komeen — Griffin, and

treatment.

others.

Apply in spring and early summer

Herbicide use information: For

during the time weeds start to

use in lakes, private farm, fish and

grow. Do not apply to more than

fire ponds; fish hatcheries; potable

third to half of a lake or pond in

water reservoirs, irrigation systems,

any one month because of excess

and stock tanks (Stocktrine). Apply

decaying vegetation which may

to control algae including Chara,

deplete oxygen content of water,

Spirogyra, and Cladophora. Chelates

killing fish. Do not apply to waters

prevent precipitation of copper with

used for irrigation, agricultural

carbonates or bicarbonates in the

sprays, watering dairy animals, or

water.

domestic water supplies.

To avoid suffocation of fish due to

lack of oxygen caused by decay of 2,4-D Amine

heavy infestations treat only a third Product and Manufacturer:

to half of the lake or pond at a time. Several

Water treated with this product Herbicide use information: For

may be used for drinking, livestock use to control aquatic weeds and

watering, swimming or fishing weeds adjacent to water. Apply for

immediately after treatment. Water control of annual weeds, perennial

treated with this product also may weeds, and woody plants. Do not

be used to irrigate turf, ornamental apply to more than a third to half

plants, or crops immediately after of a lake or pond in any one month

treatment. Copper chelates may

19

Herbicide Use

because excess decaying vegetation ditches: bladderwort, coontail, elodea,

may deplete oxygen content of water, naiad, pondweeds, and watermilfoil.

killing fish. Do not apply to waters Other aquatic weeds controlled

used for irrigation, agricultural include duckweed, cattails, and some

sprays, watering dairy animals, or filamentous algae.

domestic water supplies.

Endothall

Diquat Products and manufacturers:

Products and manufacturers: Aquathol and Hydrothol 191 —

Reward — Syngenta and Cerexagri.

Weedtrine D — Applied

Herbicide use information:

Biochemists.

Aquathol and Hydrothol 191 are

Herbicide use information: May different formulations of endothall

be fatal if swallowed, inhaled or and are both available as granular

absorbed through skin. Skin contact or liquid formulations. Hydrothol

will cause severe skin irritation. Do controls most algae and submersed

not get material on skin, eyes, or plants, but is toxic to fish at

clothing. Contact with skin may dosages in excess of 0.3 ppm.

increase danger of absorption. For Aquathol controls most submersed

application only to ponds, lakes, and plants and is not toxic to fish, but

drainage ditches where there is little does not control algae. Apply in

or no outflow of water and that are late spring or early summer when

totally under control of product’s user. weeds are actively growing. Do not

Diquat is rapidly absorbed by use treated water for irrigation,

aquatic plants and begins to work agricultural sprays, livestock, or

immediately upon contact. Plant domestic purposes for at least 7 to

tissue is destroyed, causing wilting 25 days after treatment.

and loss of foliage. Do not use treated

water for animal consumption, Fluridone

spraying, or irrigation for 14 days Product and manufacturers:

after treatment. Do not apply within Sonar AS and Sonar SRP

¼ mile of any functioning potable — SePRO, Avast — Griffin,

water intake. Whitecap-Novasource.

Treatment of dense weed areas Sonar use information: For

can result in oxygen loss from management of aquatic weeds in

decomposition of dead weeds. Treat fresh water ponds, lakes, reservoirs,

only a third to half of the dense drainage canals, and irrigation

weed area at a time to avoid fish canals. Sonar is absorbed from

suffocation from oxygen loss and wait water through leaves and shoots,

10 to 14 days between treatments. and from hydrosoil by the roots.

Do not apply to muddy water. Apply Sonar causes chlorosis at the

diquat in early season to control terminal bud or growing points

submersed weeds before weed of plant, and then plants slowly

growth has reached surface. Diquat deteriorate. Complete weed

will control the following submersed removal may require 30 to 90 days.

weeds infesting still ponds, lakes and Sonar AS is effective in controlling

20

Herbicide Use

duckweed; certain emersed trees listed on the label. Aquatic

weeds including spatterdock and plants controlled include cattails,

waterlily; certain submersed weeds annual and perennial smartweeds,

including bladderwort, coontail, spatterdock, and willow. Perennial

elodea, naiads, pondweeds, and plants generally are best controlled

watermilfoil; and certain shoreline when treated during the flowering

grasses. Sonar provides partial stage of growth. Do not apply this

control of certain vascular aquatic product within 1/2 mile upstream of

weeds including American lotus, potable water intakes, unless intake

arrowhead, cattail, rush, and is turned off for a minimum of

smartweed. 48 hours after application.

For best results, apply Sonar before

initiation of weed growth or when Imazapyr

weeds begin actively growing. Product and manufacturer:

The Sonar label indicates users Habitat — BASF.

must consult with appropriate

Habitat use information: For

state or local water authorities

control of most emerged and

before applying this product. Do

floating plants in and around

not apply in lakes, ponds, or other

standing or flowing water. Habitat

bodies of water where crayfish

does not control plants which are

farming is performed. There are no

completely submerged or that

label restrictions against swimming

have a majority of foliage under

or fishing in water treated with

water. Apply in combination with

Sonar. There are no restrictions on

a nonionic surfactant approved for

consumption of treated water by

aquatic sites as directed on the label.

humans, pets, and livestock.

Habitat is a systemic herbicide that

can be absorbed through the foliage

Glyphosate or roots of plants. Plants will stop

Product and manufacturer: growing soon after application,

Rodeo — Dow AgroSciences, but may not show symptoms or

and others. die for several days or weeks after

Glyphosate use information: This treatment. Unintended application

product may be used in and around to the foliage or soil where roots of

aquatic sites, including all bodies of desirable plants occur can result in

fresh and brackish water, which may severe injury or death of the plants.

be flowing, non-flowing or transient. There are no restrictions on the use

This includes lakes, rivers, streams, of water treated with Habitat for

ponds, seeps, irrigation and drainage recreation purposes or consumption

ditches, canals, reservoirs, and similar by livestock. Water treated with

sites. There is no restriction on use Habitat may not be used for

of water for irrigation, recreation, or irrigation purposes until 120 days

domestic purposes. Apply Rodeo after application. Do not apply this

product within 1/2 mile upstream of

plus nonionic surfactant approved

potable water intakes, unless intake

for aquatic sites as directed on the

is turned off for a minimum of 48

label to control or partially control

hours after application. Currently

marginal weeds, woody brush, and

this product is approved for use

21

Herbicide Use

only by state and federal agencies Aquatic dyes

or certified aquatic pest control

applicators who are authorized by Product and manufacturer:

state or local governments. Aquashade — Applied

Biochemists, and others.

Triclopyr Aquatic dye use information:

These products are a mixture of

Product and manufacturer:

blue and yellow dyes that intercept

Renovate — SePRO.

light penetration in water. Aquatic

Renovate use information: For dyes do not directly control the

control of certain submersed, plants through herbicidal activity,

emersed, and marginal plants but limit growth of plants below

in and adjacent to aquatic sites the water surface through shading

with minimal outflow. Apply effect. Primarily for control of

in combination with a nonionic submersed, rooted weeds, and

surfactant approved for aquatic some algae. Should only be used

sites as directed on the label. There in bodies of water with little or no

are no restrictions on the use of through-flow, in order to maintain

water treated with Renovate for dye concentration. Products should

recreation purposes or consumption be applied before foliage reaches

by livestock. Water treated with the water surface. These products

Renovate may not be used for are nontoxic to fish, wildlife,

irrigation purposes until 120 days livestock, humans, and turf. Do not

after application. Refer to the label use where water is used for human

for grazing restrictions following consumption. Safe for swimming

applications to terrestrial sites. after complete dispersal. May be

undesirable to some individuals due

to artificial appearance of water.

NPDES (National Pollutant

Discharge Elimination System)

permits maybe required for

pesticide applications to and around

water. The state contact at the

Kansas Department of Health and

Environment is Don Carlson at

(785) 296-5547.





Environmental Considerations

The general considerations, restrictions, and problems mentioned

earlier in the herbicide section also apply to other chemical usage.

The use of the water and fish must be considered. Directions and

restrictions on the pesticide label must be followed.

The publication contains common names and trade names for

herbicides. No endorsement of named products is intended nor

criticism implied of similar products which are not mentioned.



22

Herbicide Use

Study Questions 5. 2,4-D low-volatile ester

________ can be applied to

These study questions are to aid control weeds in ponds and lakes.

you in learning the material on

pages 15 through 22. a. amine 4

1. The improper application rate of b. granules

herbicides in aquatic pest control c. LV4

can adversely affect: d. postemergence herbicide

a. irrigation water. 6. Do not use Diquat treated water

b. drinking water. for animal consumption, spraying

c. fish. or irrigation for ____ days after

treatment.

d. all of the above.

a. 5

2. Improperly calibrated equipment

can cause: b. 9

c. 14

a. a faulty application.

d. 20

b. increased toxicity to fish and

other nontarget organisms. 7. Aquashade contains a mixture of

c. safe application of the _________ dyes that intercept

herbicide. light penetration in the water.

d. both a and b. a. orange and black

3. Treat ____ of a lake or pond at b. blue and yellow

any one time with Cutrine-Plus c. red and green

Algaecide to avoid suffocation of d. purple and white

fish due to oxygen depletion.

8. Water treated with Imazapyr

a. 0.1 to 0.2 or Triclpyr can not be used for

b. 0.3 to 0.5 irrigation until ____ days after

c. 0.6 to 0.8 application.

d. 0.9 to 1.0 a. 5

4. Copper sulfate is not effective b. 25

against _________. c. 30

a. single-filament algae. d. 120

b. submersed leafy weeds.

c. emersed leafy weeds.

d. both b and c.









23

Nuisance Animal

Regardless of the chemical used,

Control care must be taken to avoid

Occasionally the presence or exposure to nontarget organisms

activity of a type of animal and treated water must be

interferes with the management isolated to prevent contamination

objective for a body of water. of other water. Always follow

Such animal species are normally label directions and precautions.

present in the system but become The application of unapproved

too abundant, thus posing a compounds could lead to water

problem, or they may be species and soil contamination, kills of

that invade the body of water and desirable organisms, and residues

their activities cannot be tolerated. in fish flesh.

This section presents some of the

Nuisance Invertebrate Species

more common problems created

Zebra mussels – Zebra mussels

by nuisance aquatic animals and

(Dreissena polymorpha) usually

discusses control methods.

are less than an inch long with a

D-shaped shell and tend to resemble

Invertebrates small clams. They use sticky byssal

Certain invertebrates, other than threads to attach tightly to any

parasite and disease organisms of surface. The problem is they can

fishes, can become problems in attach to any solid substrate. The

ponds and lakes used for recreation zebra mussel is responsible for

or for aquaculture. clogging pipes at water treatment

plants. They also filter large amounts

In some cases snails may become

of water, in order to eat plankton,

the intermediate host for the

which can lead to algal blooms

parasite that causes swimmer’s

and affect native populations of

itch. It may be impractical to break

mussels. Zebra mussels are found in

the cycle by eliminating the final

many water bodies in Kansas. Their

hosts (ducks and muskrats), but

spread can be prevented with proper

partial control can be achieved

precautions. Zebra mussels are

by reducing the snail population.

spread primarily by the recreational

This can be done chemically by

activities. They can attach to a

copper sulfate used at the same

boat’s hull and trailer. This is why it

dosage for control of algae. Non-

is important to drain all the water

chemical control methods include

from boats, live wells, and bait wells.

controlling aquatic vegetation and

Wash the equipment in 140-degree

stocking with snail eating fish,

water to help insure that you are

such as catfish and redear sunfish.

not responsible for transporting this

Predaceous aquatic insects and pest. Chemicals can be used to kill

crayfish are often a problem in zebra mussels, but the chemicals will

aquaculture ponds that are stocked also have negative effects on fish and

with newly hatched fish (fry). If native mussels.

these predators are not controlled,

The rusty crayfish (Orconectes

fish survival may be very low.

rusticus) and New Zealand

Various chemicals are effective in

mudsnails (Potamopyrgus

controlling aquatic insects.

antipodarum) are invertebrates

24

Nuisance Animal

that have the potential to become necessary to completely remove

invasive species in Kansas. Rusty the fish population and start Control

crayfish have large black-tipped over. Complete removal can be

claws and colored spots on the accomplished by draining the body

carapace. If they are found in of water or by chemical treatment.

Kansas, they could potentially Chemical removal of fish

displace native crayfish and destroy populations is a widely practiced

plant diversity. The New Zealand management procedure applied to

mudsnail has brown or black cone- ponds and lakes used for recreation

shaped shells with five whorls. It or for aquaculture.

has the ability to reproduce quickly

Many chemicals are toxic to

resulting in large densities, which

fish, but most of these affect

compete with native invertebrates

nontarget organisms, cause

and fish. Report sightings of these

environmental contamination,

species to the Kansas Department

or later show up as residues in

of Wildlife and Parks (KDWP).

fish flesh. A few chemicals have

Further information about any of

undergone the testing required for

the aquatic nuisance species can be

registration. Table 3 gives approved

obtained from the KDWP website

formulations of the chemicals

at http://www.kdwp.state.ks.us/

approved as fish-control agents.

news/Fishing/Aquatic-Nuisance-

Species. Invasive Fish Species

Kansas has five invasive fish species

Fish to watch for in aquatic environments

Fish populations frequently as well as others that are emerging.

become unproductive from either These fish threaten the health of

an overabundance of stunted Kansas aquatic ecosystems because

desirable fish or contamination they outcompete native fish for

by undesirable fish species. food and space. To help prevent

Adjustment of the fish population their spread, it is important to be

may bring it back into a productive aware of these fish species and their

situation. Other times it may be identifiable features.





Table 3. Fish Control Agents Registered or Approved for Aquatic or Fishery Uses

Fish Control Agent Fishery Use Application Rate Comments

Treatment rate dependent

on water temperatures and

1-10 ppb active ingredient

Antimcycin Piscicide pH. Not approved for use

(0.4-4.3 fl. oz./acre foot)

on fish intended for human

or animal consumption.



Do not use in waters colder

than 65 F. Not approved

1-5 ppm active ingredient

Rotenone (Restricted) Piscicide for use on fish intended

(2.7-13.6 lb./acre foot)

for human or animal

consumption.



25

Nuisance Animal

White Perch – White perch (Morone species can reach more than 60

Control americana) are usually less than 10 pounds in weight and 4 feet in

inches long with a variable coloring, length. Asian carp grow quickly

but they are generally silvery green on and have a voracious appetite. They

the sides. They resemble the native directly compete with other fish for

white bass without looking at their food resources. Do not release these

characteristic differences. Walleye fish back into the water.

and white bass populations have been

Ruffe and Round Goby – The

negatively impacted by this species.

ruffe (Gymneocephalus cernuus)

This fish can hybridize with the

and the round goby (Neogobius

white bass. White perch are spread

melanostomus) are both nuisance

by illegal release into other bodies of

species that have not been found

water. If you catch a white perch, do

in Kansas. The ruffe can resemble

not release them back into the water,

young walleye, sauger, or saugeye.

instead eat or dispose of them.

The ruffe has a large continuous

Rudd – Rudd (Scardinius dorsal fin, which has spots between

erthtophthalmus) is similar in its rays. The round goby has a

appearance to a golden shiner. large head, soft bodies and dorsal

They can get up to 14 inches fins without spines. They kind of

long with dark grey back, silver resemble large tadpoles. Anglers

sides, and blood-red fins. This fish may be the first to discover

affects spawning areas for other these fish because they are both

species because they consume commonly caught by hook and

vegetation. Rudd may hybridize line. Report any sighting of these

with the golden shiner. Rudd can species to the Kansas Department

be spread by anglers accidently of Wildlife and Parks. Further

using them as bait. Anglers need information about any of the

to learn to identify the rudd aquatic nuisance species can be

and make sure they dispose of obtained from the KDWP website

unwanted bait on land. Early at: http://www.kdwp.state.ks.us/

detection of isolated populations news/Fishing/AquaticNuisance-

may help prevent their spread. Species.

Rudd are currently only found in

two locations in Kansas. Amphibians

Asian Carp – The bighead carp Amphibians are generally

(Hypophthalmichthys nobilis), black beneficial to the aquatic

carp (Mylopharymgodon piceus), and environment and are desired. In

the silver carp (Hypophthalmichthys certain situations, salamanders and

molitrix) are all species of Asian bullfrogs can become a problem

carp that can be found in Kansas. in fish culture ponds. There are no

Bighead and silver carp have low- pesticides registered for control of

set eyes and a large upturned mouth these animals. Control is limited to

without barbells. These two species physical means in compliance with

also have a scaleless head and very Kansas Department of Wildlife

small scales on the body. The black and Parks regulations.

carp has a blackish brown body

with large scales. Adults of these

26

Nuisance Animal

Reptiles Mammals Control

Aquatic turtles and snakes are The aquatic mammals that

common components of the cause the greatest problems are

aquatic ecosystem. In general they the rodents, such as beavers and

do not cause any problem to the muskrats. These rodents cause

fish population, and if left alone, damage by burrowing into dikes,

do not injure humans. In certain levees, and dams. This weakens the

situations some humans may structures often causing cave-ins,

find them annoying and in some leaks, and increases bank erosion.

aquaculture ponds they may reduce Also their damming activity can

fish production. There are no clog culverts, overflow structures,

pesticides registered for the control and streams.

on aquatic reptiles. Control can The best control methods

usually be accomplished by fishing, involve trapping during the

trapping, and shooting. Before legal furharvesting season.

control is attempted, the current Other nonchemical methods

Kansas Department of Wildlife include reducing the food supply,

and Parks regulations should installing protective barriers, and

checked and followed. shooting. Chemical control may

consist of the use of repellants

Birds and fumigants. If using control

Birds usually add to the esthetics of methods other than trapping

a body of water. In rare situations, during the legal season contact the

aquatic birds can become a problem. Kansas Department of Wildlife

Excessive waterfowl in a recreational and Parks or the wildlife damage

pond or lake can cause disturbance control specialist, Kansas State

and/or excessive nutrient enrichment University, for details on current

of the water with their wastes restrictions.

(eutrophication). In aquaculture

ponds and lakes, fish-eating birds

can have a significant impact on the

fish mortality. In both these types

of situations, the migratory bird

species involved are protected by

state and federal law. Any control

measure must be preceded by

acquiring the proper permits. Obtain

a permit from the U. S. Fish and

Wildlife Service or check with the

Kansas Department of Wildlife and

Parks or the K-State Research and

Extension wildlife control specialist

for permit procedures.









27

Nuisance Animal

Control Study Questions 5. There are _____ chemicals

approved for the control of

These study questions are to aid amphibians and aquatic reptiles.

you in learning the material on a. no

pages 24 through 27.

b. two

1. Snails can be controlled with: c. five

a. chemicals. d. seven

b. catfish. 6. Aquatic nuisance species can have

c. redear sunfish. an impact on:

d. all of the above. a. other fish populations.

2. Fish populations become b. aquatic ecosystems.

unproductive from: c. terrestrial ecosystems.

a. overabundance of stunted d. both a and b.

desirable fish.

7. Excessive waterfowl in

b. contamination by undesirable recreational ponds/lakes and fish

fish species. eating birds in aquaculture ponds/

c. a and b above. lakes are usually classes of:

d. too much food. a. song birds.

3. In controlling fish, many chemicals b. soaring birds.

are toxic but: c. migatory birds.

a. most affect nontarget d. aqua avian foul.

organisms.

8. Aquatic mammals that cause the

b. cause environmental greatest problems in Kansas are:

contamination.

c. show up later as residues a. muskrats.

in fish. b. beavers.

d. all of the above. c. escaped polar bears.

4. The aquatic nuisance species that d. a and b above.

resembles the golden shiner is the:

a. Rudd.

b. Asian carp.

c. Ruffe.

d. none of the above.









28

Parasites and

Diseases of Fish

Fish in nature have a wide variety quality water and good nutrition

of parasites and diseases. Usually usually result in healthy fish.

these do not have a major impact Healthy fish are usually resistant to

on the fish populations. When diseases.

fish are crowded and placed under

At times parasite and disease

stressful conditions, as in the

problems occur that can best be

intensive culture of conservation

treated with a chemical. Treatment

agency fish hatcheries and private

compounds themselves can be

aquaculture, parasites and diseases

potentially hazardous to the fish

can become a serious problem.

if used improperly. The details of

The best treatment, of course, diagnosis and treatment are highly

is prevention. Sound culture technical and require additional

management including good training so they will not be covered



Table 4. Approved Drugs Used in Aquaculture

Active Drug Supplier Fishery Use Application Rate Comments

Formalin Natchez Control of external 25 ppm in ponds (7.5 Drug must not be

(Formalin-F, Animal Supply protozoa and gals./acre foot) subjected to temperatures

Paracide-F, Company, Argent monogenetic 125–250 ppm in tanks below 40 degrees F.

Parasite-S and Laboratories, Inc., trematode parasites in (1–2 pints per 1000 There is no mandatory

Formacide-B) Western Chemical, finfish, salmon, trout, gals) for one hour withdrawal time prior

Inc., B. L. Mitchell, catfish, largemouth to food or non-food fish

Inc. bass, and bluegill. 1,000–2,000 ppm for harvest. Use in warm

Control of fungi 15 minutes for egg weather may cause oxygen

family Saprolegniaceae treatment depletion. Provide aeration

on eggs. Control of during treatment to

external protozoan prevent low oxygen.

parasites on penaeid

shrimp.







MS-222: tricaine Argent Anesthetic – Temporary 10–1,000 mg/L 21-day preslaughter

methane-sulfonate Laboratories, immobilization of interval. Water

(Finquel, Western Chemical, aquatic cold-blooded temperature over 50

Tricaine-S) Inc. animals and fish. degrees F.

Oxyytetracycline Phibro Animal Bactericide – Treat 2.5 3.75 g/100 lbs. of Withdrawal time of

dehydrate Health diseases in catfish, fish per day for 5 days 21 days for catfish and

(Terramycin 200) salmonids, and lobster. in feed salmonids and 30 days for

lobster. Check for specific

temperature restrictions.





Ormetropin + Aquatic Health Bactericide – Treat 2.3 g. active 3-day withdrawal time for

Sulfadimethoxine Resources enteric septicemia ingredient/100 lb. fish catfish, 42-day withdrawal

(Romet 30 and of catfish and per day for 5 days time for salmonids. Use in

Romet TC) furnuculosis in feed.

salmonids.

(continued)

29

Parasites and

in this manual. Few chemicals are future losses. It is important to

Diseases of Fish registered for use on food fish. know how water volume, flow,

Table 4 gives the approved drugs or quality influences treatment

available for use in aquaculture. efficacy. Treatments must be

Treatments can be classified as handled properly and safely to

either therapeutic or prophylactic. protect workers as well as the

Therapeutic treatments are used treated fish. It is also important to

to reduce losses from an ongoing know the level of chemical in the

disease, while prophylactic hatchery effluent.

treatments are preventative against







Table 4. Approved Drugs Used in Aquaculture (continued)

Active Drug Supplier Fishery Use Application Rate Comments

Florfenicol Intervet Schering- Control of mortality 10 mg per kg fish for Veterinary Feed Directive

(Aquaflor) Plough Animal due to enteric 10 days (VFD) drug. 12–15 day

Health Corp. septicemia or withdrawal interval

columnaris disease depending on fish species.

in catfish. Control

of mortality in

salmonids due to

coldwater disease or

funrunculosis.

Oxytetracycline IVX Animal Mark skeletal tissues 200–700 mg per L of None

HCL Health, Aquatic in finfish fry and water for 2-6 hours

(Oxytetracycline Health Resources, fingerlings.

HCL Soluble Bimeda

Power-343,

Terramycin 343,

Tetroxy

Hydrogen Peroxide Western Chemical Control of mortality 500–1,000 mg per L Initial bioassay on a

(35 % Perox-Aid) Inc. due to saprolegniasis depending on type small number of fish

in finfish eggs. Control of water and system recommended before

of mortality due for finfish eggs. 50– treating the entire group.

to bacterial gill in 100 mg per L for 60 0 day withdrawal time.

salmonids and control min. once per day on

of mortality dye to alternate days. Consult

external columnaris in the label for specific

catfish. directions.

Chorionic Western Chemical Aid in improving Consult veterinarian. Intramuscular injection.

gonadotropin Inc. spawning function. Prescription product

(Chorulon) restricted to use by or on

the order of a licensed

veterinarian.









30

Parasites and

Study Questions 3. The drug __________can only be

Diseases of Fish

used by or on the order of a licensed

These study questions are to aid veterinarian.

you in learning the material on

pages 29 through 30. a. Terramycin 200

1. The best treatment for fish diseases b. Chorulon

and parasites is: c. Aquaflor

a. prevention. d. Both b and c

b. mechanical removal. 4. A bactericide used to treat diseases

c. chemical removal. in fish is:

d. bright lights. a. Romet 30.

2. What type of treatment is used to b. acetic acid (vinegar).

prevent an outbreak of a disease? c. formalin.

a. therapeutic d. none of the above.

b. INAD use

c. prophylactic

d. all of the above









31

Calculations

Volume

Most herbicides are applied on

Proper chemical treatment requires the basis of volume as a certain

accurate determination of the area number of parts per million (ppm)

and volume of the body of water. or as a certain amount per acre-

foot (1 acre of surface water that

Area is 1 foot deep). To find volume,

Some chemicals are applied at a determine average depth by taking

Table 5. Conversion Units

certain rate per surface area (square numerous evenly spaced depth

and Equivalents

feet or acres). Surface area can be measurements. The accuracy of the

1 acre- = 1 acre of surface water 1 foot determined with the use of aerial average depth estimate increases

foot deep photographs, global positioning the more depth measurements

= 43,560 cubic feet of water system (GPS) measurements, or taken. Shallow measurements must

= 2,718,144 pounds of water actual measurements. Calculate be included or the estimate will be

= 326,000 gallons of water area by multiplying average length too high.

1 cubic = 7.5 gallons times average width. This is easy

Multiply calculated average depth

foot = 62.4 pounds of water if the body of water is rectangular

by the surface area determined

= 28,355 grams of water or oval in shape. If a more accurate

by the method described earlier.

estimate is desired, or if the body

1 gallon = 8.34 pounds of water If all measurements were made

of water is an irregular shape, use

= 128 fluid ounces in feet, the calculated volume

the graph paper method.

= 3,785 milliliters or cubic will be in cubic feet. Use this

centimeters number to calculate the amount of

Measure length and width

= 3,785 grams of water

in several places. Transfer herbicide product recommended

1 cubic = 7.5 gallons per second

measurements onto a sheet of on the label. Aquatic herbicide

foot per

second

= 450 gallons per minute

graph paper according to a scale. application is often expressed on

(cfs) = 28.3 liters per second

Draw the shoreline with the a per acre-foot basis, but can be

1 quart = 946 milliliters or cubic proper curvatures. Determine changed to the units expressed on

centimeters

the area by counting the squares the label by using the conversion

= 946 grams of water and multiplying by the scale area table (Table 5). Dosage amounts

1 pound = 453.6 grams (454) for each square. For example: can be determined with the

= 16 ounces if the scale is such that the side formulas given in Table 6, page 33.

1 ounce = 28.35 grams of one square is 5 feet, then the

1 part per 2.7 pounds per acre foot area of one square is 5 × 5 or 25 Flow

million 0.0038 grams per gallon square feet. The area then can be If a chemical must be applied to

(ppm) flowing water (canal or stream) the

requires 0.0283 grams per cubic foot expressed as square feet or acres.

0.000062 pounds per cubic One acre = 43,560 square feet. flow rate needs to be determined.

foot Based on the concentration desired

Surface area of pond in acres = in the water, calculate the chemical

1 milligram per liter

pond area in square feet introduction rate using formulas

43,560 given in Table 7, page 33.



Calculate the flow rate by picking

a section of the canal or stream

with straight sides and a fairly

even bottom to take the necessary

measurements. Measure width

and a transect of evenly spaced

32

Calculations

depth measurements. Muliply factor equals 0.9; for a rough or

width times the average depth rocky bottom this factor equals 0.8.

to get the cross section area. The

surface velocity of the flow should Because of the flowing nature

be measured at several places along of treated stream, the chance of

this transect to get the average contaminating nontreatment areas

velocity. This can be done by is very high. A detoxification

timing an object as it flows over a program may have to be

measured distance of several feet incorporated into the treatment

or using a flow meter. program. Also, due to the

difficulty of accurate stream

Multiply the velocity in feet per flow determinations and length

second by the cross section area of time to treat, the applicator

(in square feet) to get flow in should check with the state fish

cubic feet per second (cfs). Then and game agency and/or the

multiply by a bottom friction state department of health and

factor (a) to reduce the amount. environment before treating any

For a smooth, even bottom this flowing water.





Table 6: Table of Formulas Used in Chemical Application to Ponds and Lakes



Volume of pond in cubic feet = surface area in square feet × average depth in feet

volume of pond in cubic feet

Volume of pond in acre feet =

43,560

Total ponds of active ingredient (a.i.) required = acre feet × 2.7 × ppm desired

amount of active ingredient to apply × 100

Amount of formulation to apply =

% of a.i. in formulation

acre feet × 2.7 × ppm desired

Total gallons of formulations required =

pounds a.i. per gallon of formulation





Table 7: Table of Formulas Useful in Chemical Applications to Flowing Water



Cross section area of channel in square feet = width in feet × average depth in feet

Stream flow in cubic feet per second (cfs) = cross section in square feet × average velocity in feet per second

× friction factor (a) a = 0.9 in smooth bottom, 0.8 in rough

bottom

Pounds of active ingredient (a.i.) per cfs = ppm desired × 0.0000623.

ppm desired × stream flow in cfs × 60 (sec/min) × 0.0000623 × 100

Pounds of formulation per minute =

% of active ingredient in formulation









33

Calculations

Example problems

Pond volume: A pond is measured to have an average length of 210 feet,

an average width of 120 feet, and an average depth of 3.3 feet. What is

the volume in acre feet?

210 feet × 120 feet × 3.3 feet

Volume = = 1.91 acre feet

43,560 cubic feet/acre feet



Pond treatment: A pond needs to be treated for aquatic vegetation. The

label states that 4.5 pounds of the material is needed per acre foot. The

volume of the pond is 3.1 acre foot. How many pounds of the material

should be applied?

Pounds to be applied = 4.5 pounds/acre feet × 3.1 acre feet = 14 pounds



Pond treatment: A pond needs to be treated at a rate of 2 ppm active

ingredient. The volume of the pond is 4.2 acre feet. The chemical is

available as a 25% active ingredient formulation. How many pounds

of the formulation should be applied for proper treatment?

(1 ppm = 2.7 pounds/acre feet)

Pounds of formulation =

2 ppm × 4.2 acre feet × 2.7 pounds/acre feet × 100

= 90.7 pounds

25%



Stream flow: A stream is 9.6 feet wide, has an average depth of 1.8 feet,

a flow velocity of 1.2 feet per second, and a smooth bottom. What is the

stream flow in cfs?

Stream flow = 9.6 feet × 1.8 feet × 1.2 feet/sec × 0.9 = 18.66 cfs



Stream treatment: A canal needs to be treated at 1 ppm active

ingredient. The chemical comes as an 80% formulation. The canal has a

flow of 20 cfs. How many pounds of this formulation should be metered

into the canal each minute?

Pounds of formulation =

1 ppm × 20 cfs × 0.0000623 pounds per cubic foot × 100

= 0.093 pounds per minute

80%









34

Calculations

Study Questions 3. What do the initals cfs stand for?

These study questions are to aid a. chemical formulation standard

you in learning the material on b. cubic foot per second

pages 32 through 34. c. cubic feet in streams

1. The area of a lake or pond can be d. none of the above

determined by: 4. In order to determine the flow

a. aerial photographs. rate of a stream, the necessary

b. multiplying average length by measurements include:

average width. a. stream width.

c. several measurements b. surface velocity.

transferred to graph paper. c. stream depth.

d. all of the above. d. all of the above.

2. The most important thing in

determining the volume of a body

of standing water is:

a. subtracting the volume of fish.

b. taking numerous, evenly

spaced depth measurements.

c. subtracting the volume

of algae.

d. measuring the flow rate.









35

Additional

Guide to Drug, Vaccine, and

Information Pesticide Use in Aquaculture. 2007

Additional information on aquatic revision, http://aquanic.org/jsa/

plants and their control is available wgqaap/drugguide/drugguide.htm.

from the following sources: Accessed February 1, 2010.

1. K-State Research and Extension Kansas Department of Wildlife

www.ksre.ksu.edu and Parks. 2009. Aquatic

Nuisance Species. http://www.

2. Kansas Department of Wildlife

kdwp.state.ks.us/news/Fishing/

and Parks

Aquatic-Nuisance-Species. Accessed

www.kdwp.state.ks.us

February 1, 2010.

3. Kansas State University Weed

National Aquaculture Association.

Management

2003. Drugs and Chemicals

www.agronomy.ksu.edu/

in US Aquaculture: http://

extension/DesktopDefault.

www.thenaa.net/downloads/

aspx?tabid=69

Drugs_and_Chemicals_in_US_

4. Missouri Department of Aquaculture_11.10.pdf. Accessed

Conservation February 1, 2010.

mdc.mo.gov/nathis/plantpage/

Peterson, Dallas E. and Charles

flora/wetplant

Lee, 2005. Aquatic Plants and

5. Texas A&M Aquaplant Their Control. Kansas State

aquaplant.tamu.edu University, Manhattan, Kansas.

USDA, NRCS. 2010. The

References PLANTS Database. National

Aquatic, Wetland, and Invasive Plant Data Center, Baton Rouge,

Plants Line Drawings, 1990. LA. http://plants.usda.gov.

IFAS, Center for Aquatic Plants, Accessed February 1, 2010.

University of Florida, Gainesville, USFWS AADAP Program,

FL. http://plants.ifas.ufl.edu/ the AFS Fish Culture Section,

node/482. Accessed February 1, AFS Fish Health Section, and

2010. FDA Center for Veterinary

Burtle, Gary J. 2009. Aquatic Medicine. 2008. A Quick

Environments: Fishery Chemicals Reference Guide To: Approved

– (Parasites, Piscicides and Other Drugs for Use in Aquaculture:

Treatments) http://www.ent. http://www.fda.gov/downloads/

uga.edu/pmh/Com_Aquatic.pdf. AnimalVeterinary/ResourcesforYou/

Accessed February 1, 2010. AnimalHealthLi%20teracy/

UCM109808.pdf. Accessed

February 1, 2010.









36

Answers to Study Questions

Pages 3–13

1. d, 2. d, 3. b, 4. c, 5. d, 6. d, 7. b, 8. d

Pages 15–22

1. d, 2. d, 3. b, 4. d, 5. b, 6. c, 7. b, 8. d

Pages 24–27

1. d, 2. c, 3. d, 4. a, 5. a, 6. d, 7. c, 8. d

Pages 29–30

1. a, 2. c, 3. d, 4. a

Pages 32–34

1. d, 2. b, 3. b, 4. d



37

Notes









38

Frannie L. Miller

Pesticide Coordinator

Dallas E. Peterson

Weed Specialist, Agronomy

Charles D. Lee

Wildlife Specialist, Animal Sciences and Industry

Acknowledgments

Appreciation is expressed to the following for cooperation

in the Commercial Pesticide Application Training Program:

Jeanne Fox, Certification and Training Section Chief,

Pesticide and Fertilizer Program, Kansas Department of Agriculture

Illustrations

USDA-NCRS, National Plant Data Center

IFAS, Center for Aquatic and Invasive Plants, University of Florida





Brand names appearing in this publication are for product identification purposes only.

No endorsement is intended, nor is criticism implied of similar products not mentioned.

Publications from Kansas State University are available on the World Wide Web at: www.ksre.ksu.edu

Publications are reviewed or revised annually by appropriate faculty to reflect current research and practice.

Date shown is that of publication or last revision. Contents of this publication may be freely reproduced

for educational purposes. All other rights reserved. In each case, credit Frannie L. Miller,

Aquatic Pest Control, Kansas State University, October 2010.









Kansas State University Agricultural Experiment Station and Cooperative Extension Service

S-29 October 2010

K-State Research and Extension is an equal opportunity provider and employer. Issued in furtherance of Cooperative Extension Work, Acts

of May 8 and June 30, 1914, as amended. Kansas State University, County Extension Councils, Extension Districts, and United States Department

of Agriculture Cooperating, Gary Pierzynski, Interim Director.



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