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Vol. 15—1961 - NorthEastern Weed Science Society

Vol. 15—1961 - NorthEastern Weed Science Society

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529.<br />

As an algicide we have been using 2,3-Dichloronaphthoquinone (Phygon<br />

XL). This is a selective algicide and will not produce, in our opinion, the<br />

clarity of water that copper sulphate does, Within the fish kill liniits.<br />

There are certain well established critical temperatures of fresh water that<br />

stimulate certain species of algae into activity. We watch for 68 degrees<br />

Fahrenheit and 77 degrees Fahrenheit. However, we are not attempting to<br />

destroy all algae, as we try to run off as much as possible in suspension.<br />

Moreover it protects our fish life. Our costs for algae treatment l~re formerly<br />

higher than the cost for weed treatment. Now algae control expenditures<br />

are one-third of the present cost of weed treatment. We must advise that<br />

we have to face up to some complaints about algae following the weed kill,<br />

but there is an understanding acceptance, in view of the overall objective.<br />

The dichlone is applied by the same equipment as the sodium arsenite<br />

with minor changes. We mix fifty pounds of the powder with one hundred gallons<br />

of lorater. The liquid is drawn from the tank by a twenty gallon per<br />

minute pump. A "y" connection is used to direct one outlet approXimately 45<br />

degrees off the port stem and the other 45 degrees off the starboard stern.<br />

To produce a spray pattern two short lengths of ordinary garden hose with<br />

adjustable nozzles are used. An effective mix is obtained ,men the spray<br />

pattern just meets the outer edges of the propeller wash. We use one pound<br />

per acre. Control and constant agitation is obtained by adjusting a by-pass<br />

valve directing a percentage of flow-back to the tank.<br />

As possibly related to our algae growth, a comment on our coliform<br />

count is interesting. Considering the potential possibilities we have of<br />

coliforn contamination, we are unusually low. We are told by a local<br />

bacteriologist; who does our analytical work in this category, that we have<br />

the ,lowest average coliform count of all northern New Jersey lakes that come<br />

under his observation - also the highest algae count. This possible relationship<br />

is supported by a paper presented at the American Public Health<br />

Association on November 3rd at San Francisco, entitled II Controlled Photosynthesis<br />

and Public Health ll , and the National Civic Review July, 1900.<br />

The rapid production of oxygen by algae acts as one of natures most powerful<br />

purifying agents. This is another reason why we have put limits on our<br />

algae kill.<br />

lVithin the boundaries of the Lake Mohawk reservation, we have a<br />

twenty-four acre pond known as Upper Mohawk. This pond is also infected<br />

with Potamogeton. crisp~s • Our treatment in this pond is the same as on the<br />

main .Lake , For sqme reason the plants grow at Upper Lake with less vigor<br />

and develop about three weeks later. In 1958 this pond was infected lrl.th<br />

Myriophyllum ·spicatum. It spread with great rapidity. By August, 1958, the<br />

growth could be seen under water throughout the entire t,,,enty-four acres.<br />

On August 20, 1958, we treated with 2,4,5-TP (Kuron) at 2 PPM; The chemical<br />

was mixed with fifty percent water in a one hundred gallon tank and was constantly·<br />

agitated by power. Application was ~de with an ordinary adjustable<br />

garden hose nozzle under light pressure. Every square foot was treated. The<br />

shore linea were simultaneously treated with a hand pump from a rowboat. The<br />

Myriophyllum was literally nipped in the bud. No evidence of this growth has<br />

re-appeared up to 1900. To prove this control, we elim1n.a.ted all treatment<br />

of either sodium arsenite or 2,4,5-TP in 1959. The 2,4,5-TP applied in<br />

August, 1958 also sharply lessened the Potamogeton growth in 1959. lIowever,

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