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Report from The Oklahoma Aquaculture Association

 

 


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April 15, 2002 - Department Of Environmental Quality  sets required Best Management Practices for fish farmers. Discharge permitting news.

At the present, the US Environmental Protection Agency (EPA) has established lower limits of aquatic animal production for inclusion in the National Pollutant Discharge Elimination System (NPDES) permitting process. The limits are one hundred thousand (100,000) pounds of warmwater, or twenty thousand (20,000) pounds of cold water aquatic animal production. For aquaculture facilities which do not require NPDES permitting and monitoring, we have compiled a list of Best Management Practices (BMPs) which in part or sum are intended to minimize pollutant loading to the aquatic environment within the state of Oklahoma. Operators of aquaculture facilities must adopt the first seven (7) of the following BMPs, and may choose any combination of the remaining list, or devise their own, as long as the goal of environmental protection is achieved.

This general permit will apply to those warmwater facilities which produce no more than one hundred thousand (100,000) pounds annually, and to cold water facilities which produce no more than twenty thousand (20,000) annually, or to warm water or cold water facilities which discharge no more than thirty (30) days annually. All aquatic animal culture facilities shall submit a copy of their BMPs and aquatic culture permit for inventory purposes, regardless of permit status. Aquaculture facilities which do not discharge culture water are exempt from the general permit.

Adoption of this list of BMPs is encouraged for all farms, regardless of NPDES permit status. These practices will minimize nutrient and sediment discharge for all farms, and enable growing farms to do so with the least disruption to meet discharge standards. We should all remember that discharge standards will probably become more stringent in the future if aquaculture is found to adversely affect the aquatic environment.

1. Ponds which must discharge directly to a stream without a settling basin should be used to culture species of sizes of fish which have minimize the potential for causing water quality problems (e.g., fry or fingerlings or low density culture of stockers or food fish). Many other BMPs can be used on these ponds to reduce turbidity (e.g., remove most fish before onset of draining, drain last water slowly, use of harvest basins, no draining while seining, etc.).

2. 2. When possible, construct structures in drainage ditches/canals to stabilize flow and allow sediment settling. Do not disturb non-woody vegetation in open drainage structures, and where possible, keep the bottom of the structures flooded to encourage the growth of aquatic vegetation.

3. Written records of pond discharges, or any activity which could disturb normal stream flows or conditions, shall be maintained. The record should include at least the following information: date and time of activity or discharge, duration of activity or discharge, volume of discharge, location of activity or discharge.

4. Aquatic culture facilities shall maintain all the Material Safety Data Sheets (MSDS) for drugs and/or chemicals used in the fish ponds, and shall maintain records of all drugs and/or chemicals used in each pond. Records shall include the amount(s) used and inclusive dates of use. Culture pond water containing chemicals and/or drugs shall not be discharged within the EPA-approved withdrawal period. Do not apply chemicals at any time or in any manner which would result in a toxic discharge.

5. Discharge the final 12 inches (30 cm) of sediment-laden pond water to a retention/settling basin, and allow sediments to settle for at least 24 hours before discharge

6. Sediments removed from ponds should be used for levee repair or to provide topsoil to denuded areas within the farm. Vegetate all exposed sediments as soon as possible to minimize erosion and discharge.

7. Storm water discharge from empty or dry ponds shall be settled before release

8. When possible, design or retrofit aquaculture farms to minimize or eliminate discharge. Total retention facilities are not subject to discharge regulations

9. Discharge pipes or ditches should be constructed to avoid erosion of pond levees, ditch embankments or beds, or stream banks or beds. Extend drain pipes beyond toes of embankments to prevent erosion of the embankments by discharge. If discharges have a vertical drop, the splash area should be protected with bedrock, rip rap or concrete

10. Construct discharge ditches/canals with adequate hydraulic cross sections and side slopes to minimize erosion, and vegetate levee slopes

11. The use of concrete or metal in-pond harvest basins will eliminate pond seining at the end of harvest operations for some species and life stages of fish. Fish will be taken from the basin, thus not stirring the bottom sediments. The basin will keep sediments away from the drain

12. Divert excess runoff from large watersheds away from the farm to minimize input of suspended solids and nutrients to the ponds or farm storm water discharge

13. Vegetate pond levees and road embankments as soon as possible after construction to prevent erosion and sediment release. Follow recommended fertilization rates for vegetative cover to minimize risk of nutrient discharge

14. Where appropriate, vegetate the interior levees and pond bottoms of ponds that are normally dried between production cycles. Close pond drains when renovating inside earthwork to prevent discharge of suspended solids after rains

15. Establish grass or other vegetation on all denuded areas of farm watershed to minimize erosion and sediment/nutrient transport

16. Do not apply fertilizer to ponds within the last week prior to draining. If manure from warm blooded animals is used to fertilize ponds, use composted manure if possible, and discharge to a vegetated retention/settling unit before discharge. Fertilize ponds only to promote plankton blooms

17. Use stocking and feeding practices that do not lead to serious water quality deterioration within ponds. Minimize accumulation of uneaten feed in ponds, and do not discharge uneaten feed

18. Use aerators to prevent low oxygen concentrations in culture ponds, but operate aerators to minimize erosion of pond bottoms and embankments

19. Store fertilizers, lime, salt and other pond amendments so they are not discharged with storm water runoff

20. When fish are harvested with seines, or when farm workers mix or wade in pond water when harvesting, harvest all fish possible before draining the ponds

21. Do not drain water while seining or wading in ponds. Avoid water discharge during final seining. Try to do final seining during the coolest part of the day to minimize activity levels of the fish which would aggravate sediment resuspension

22. Flow rates of discharged water should be managed to avoid increasing turbidity in the receiving stream

23. Pond drains should be operated to minimize sediment release.

 


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