Vol. 15—1961 - NorthEastern Weed Science Society

Vol. 15—1961 - NorthEastern Weed Science Society Vol. 15—1961 - NorthEastern Weed Science Society

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52e. There is a constant reinfection that occurs annually. The seedlings throughout the sun:mer and early fall are carried by the prevailing wind - at Lake Mohawkfrom southwest to northeast. Any protruding land acts as a seed trap. Areas that lie in the wind shadow of the prevailing wind currents hold their seedlings. It is more difficult to control seed dispersal where the prevailing wind is contrary to the 'Water flow. These conditions prevail at Upper Mohawk and nearby Lake Hopatcong. In view of the general movement of seedlings we have put one cove at the northwestern end of the lake under special observation. This area is nine acres. Due to its location and width of opening to the main lake (200 yards) this area has a lesser chance for reinfection. In 1950 every square foot was covered with Potamogeton crispus and was unusable for recreational purposes. In 1900 this area is usable at all times and an annoying insect problem has been reduced because of the high degree of weed control. For three years we have double treated this area in the manner described with the hope of exhausting the seeds stored in the bottom. In 1960this area had a very light growth and was treated but once. Although sodium. arsenite controls our main problem, its use creates an obnoxious by-product. The disintegration of the dead weeds sharply raises the bacteria, which in turn are finally reduced to fertiliZing elements that support a heavy growth of algae. We rake out as much of the dead weeds as we can through nine beaches and have persuaded many property owners to do likewise. As Lake Mohawk is man-made the lake bottom .... ras formerly farm land and pasture land and carried with it all the nutrients kindred to farming and cattle grazing. We are on a migratory flight line for birds and their fertilizing droppings. Property owners keep their lawns well fertilized and every rain storm washes in more nutrients J organic and inorganic. The evidence of persistent foam indicates that detergents are carrying organic nitrogeneous compounds into the lake. The cumulative effect fram these sources and others of nutrient material contribute heavily toward the continued support of weed and algae growth. In consideration of these factors of lake fertility we altered our algae control program in 1956. We try to run off by natural means 88 much alga laden water as possible. To maintain a constant run off we control our spillway outlet by the use of six 2 x 6" boards laid flat one on the other, as opposed to 'the eustomary gate used in small lakes. As the lake level drops, the top board is removed, thereby assuring a two-inch flow of outgoing water off' the top level of the lake where the blue green algae thrives, such as Anabaena and MY!=rocystis. In this manner we are able to flush off large quantities of algae and their resultant nutrients. \olhen there is a sharp differential between the daytime atmospheric temperature and cooler air at night, a thermal inversion occurs. The cooler water on top" due to its increased, density, segregates temporarily a greater amount of algae in the top water. This is run off' if the wind is favora.ble. '-Thenthe lake water reaches thermal equilibrium later in the day, the board is replaced to save water. By means of' a top water control we are also abl.e to fl.ush off IDaIl¥Potamogeton see

529. As an algicide we have been using 2,3-Dichloronaphthoquinone (Phygon XL). This is a selective algicide and will not produce, in our opinion, the clarity of water that copper sulphate does, Within the fish kill liniits. There are certain well established critical temperatures of fresh water that stimulate certain species of algae into activity. We watch for 68 degrees Fahrenheit and 77 degrees Fahrenheit. However, we are not attempting to destroy all algae, as we try to run off as much as possible in suspension. Moreover it protects our fish life. Our costs for algae treatment l~re formerly higher than the cost for weed treatment. Now algae control expenditures are one-third of the present cost of weed treatment. We must advise that we have to face up to some complaints about algae following the weed kill, but there is an understanding acceptance, in view of the overall objective. The dichlone is applied by the same equipment as the sodium arsenite with minor changes. We mix fifty pounds of the powder with one hundred gallons of lorater. The liquid is drawn from the tank by a twenty gallon per minute pump. A "y" connection is used to direct one outlet approXimately 45 degrees off the port stem and the other 45 degrees off the starboard stern. To produce a spray pattern two short lengths of ordinary garden hose with adjustable nozzles are used. An effective mix is obtained ,men the spray pattern just meets the outer edges of the propeller wash. We use one pound per acre. Control and constant agitation is obtained by adjusting a by-pass valve directing a percentage of flow-back to the tank. As possibly related to our algae growth, a comment on our coliform count is interesting. Considering the potential possibilities we have of coliforn contamination, we are unusually low. We are told by a local bacteriologist; who does our analytical work in this category, that we have the ,lowest average coliform count of all northern New Jersey lakes that come under his observation - also the highest algae count. This possible relationship is supported by a paper presented at the American Public Health Association on November 3rd at San Francisco, entitled II Controlled Photosynthesis and Public Health ll , and the National Civic Review July, 1900. The rapid production of oxygen by algae acts as one of natures most powerful purifying agents. This is another reason why we have put limits on our algae kill. lVithin the boundaries of the Lake Mohawk reservation, we have a twenty-four acre pond known as Upper Mohawk. This pond is also infected with Potamogeton. crisp~s • Our treatment in this pond is the same as on the main .Lake , For sqme reason the plants grow at Upper Lake with less vigor and develop about three weeks later. In 1958 this pond was infected lrl.th Myriophyllum ·spicatum. It spread with great rapidity. By August, 1958, the growth could be seen under water throughout the entire t,,,enty-four acres. On August 20, 1958, we treated with 2,4,5-TP (Kuron) at 2 PPM; The chemical was mixed with fifty percent water in a one hundred gallon tank and was constantly· agitated by power. Application was ~de with an ordinary adjustable garden hose nozzle under light pressure. Every square foot was treated. The shore linea were simultaneously treated with a hand pump from a rowboat. The Myriophyllum was literally nipped in the bud. No evidence of this growth has re-appeared up to 1900. To prove this control, we elim1n.a.ted all treatment of either sodium arsenite or 2,4,5-TP in 1959. The 2,4,5-TP applied in August, 1958 also sharply lessened the Potamogeton growth in 1959. lIowever,

52e.<br />

There is a constant reinfection that occurs annually. The seedlings<br />

throughout the sun:mer and early fall are carried by the prevailing wind - at<br />

Lake Mohawkfrom southwest to northeast. Any protruding land acts as a<br />

seed trap. Areas that lie in the wind shadow of the prevailing wind currents<br />

hold their seedlings. It is more difficult to control seed dispersal<br />

where the prevailing wind is contrary to the 'Water flow. These conditions<br />

prevail at Upper Mohawk and nearby Lake Hopatcong. In view of the general<br />

movement of seedlings we have put one cove at the northwestern end of the lake<br />

under special observation. This area is nine acres. Due to its location and<br />

width of opening to the main lake (200 yards) this area has a lesser chance<br />

for reinfection. In 1950 every square foot was covered with Potamogeton<br />

crispus and was unusable for recreational purposes. In 1900 this area is<br />

usable at all times and an annoying insect problem has been reduced because<br />

of the high degree of weed control. For three years we have double treated<br />

this area in the manner described with the hope of exhausting the seeds stored<br />

in the bottom. In 1960this area had a very light growth and was treated but<br />

once.<br />

Although sodium. arsenite controls our main problem, its use creates an<br />

obnoxious by-product. The disintegration of the dead weeds sharply raises<br />

the bacteria, which in turn are finally reduced to fertiliZing elements that<br />

support a heavy growth of algae. We rake out as much of the dead weeds as<br />

we can through nine beaches and have persuaded many property owners to do<br />

likewise. As Lake Mohawk is man-made the lake bottom .... ras formerly farm land<br />

and pasture land and carried with it all the nutrients kindred to farming<br />

and cattle grazing. We are on a migratory flight line for birds and their<br />

fertilizing droppings. Property owners keep their lawns well fertilized and<br />

every rain storm washes in more nutrients J organic and inorganic. The evidence<br />

of persistent foam indicates that detergents are carrying organic<br />

nitrogeneous compounds into the lake. The cumulative effect fram these<br />

sources and others of nutrient material contribute heavily toward the continued<br />

support of weed and algae growth.<br />

In consideration of these factors of lake fertility we altered our algae<br />

control program in 1956. We try to run off by natural means 88 much alga<br />

laden water as possible. To maintain a constant run off we control our spillway<br />

outlet by the use of six 2 x 6" boards laid flat one on the other, as opposed<br />

to 'the eustomary gate used in small lakes. As the lake level drops,<br />

the top board is removed, thereby assuring a two-inch flow of outgoing water<br />

off' the top level of the lake where the blue green algae thrives, such as<br />

Anabaena and MY!=rocystis. In this manner we are able to flush off large<br />

quantities of algae and their resultant nutrients. \olhen there is a sharp<br />

differential between the daytime atmospheric temperature and cooler air at<br />

night, a thermal inversion occurs. The cooler water on top" due to its increased,<br />

density, segregates temporarily a greater amount of algae in the top<br />

water. This is run off' if the wind is favora.ble. '-Thenthe lake water reaches<br />

thermal equilibrium later in the day, the board is replaced to save water.<br />

By means of' a top water control we are also abl.e to fl.ush off IDaIl¥Potamogeton<br />

see

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