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. Ecology of Buzzards Bay : an estuarine profile. Estuarine ecology -- Massachusetts Buzzards Bay (Bay); Ecology -- Massachusetts Buzzards Bay Watershed. 88 BIOLOGICAL REPORT 31. shallow nearshore embayments. The impact of the shellfishery (and recreational finfishery) on the ma- rine economy is much greater than value of the an- nual catch because both support secondary indus- tries and tourism. .... Fig. Spray irrigation on cranberry bogs, the primary method for application of fertilizer and pesticides, although flooding is also used for pest control. Photo by B. Howes. As commercial fi
. Ecology of Buzzards Bay : an estuarine profile. Estuarine ecology -- Massachusetts Buzzards Bay (Bay); Ecology -- Massachusetts Buzzards Bay Watershed. 88 BIOLOGICAL REPORT 31. shallow nearshore embayments. The impact of the shellfishery (and recreational finfishery) on the ma- rine economy is much greater than value of the an- nual catch because both support secondary indus- tries and tourism. .... Fig. Spray irrigation on cranberry bogs, the primary method for application of fertilizer and pesticides, although flooding is also used for pest control. Photo by B. Howes. As commercial finfishing is prohibited within Buzzards Bay waters, the marine economy most impacted by poor water quality conditions is the shellfishing industry. Unfortunately, only limited long- term information is available on local catches, and much of these data are of marginal quality for our purposes. The lack of information restricts our ability to look at long-term trends in economic losses caused by pollution or overfishing. Closures of shell- fish beds because of coliform contamination, how- ever, provide a general idea of the increased im- pact of anthropogenic activities within the water- shed (cf. Chapter 6). Although commercial marine activities do con- tribute some pollution to the bay, they also tend to be the most affected by pollution. This is particu- larly evident in the steady increase of shellfish bed closures caused by fecal coliform contamination, originating from road runoff, damaged septic sys- tems, and wildfowl and other animal wastes. The average of 1,764 ha closed to shellfishing in 1970 has steadily increased, reaching an average of 4,452- 4,856 ha in 1988 and nearly 6,070 ha in 1990. Although only a moderate portion of the overall shellfishery (primarily through recreational harvest), soft-shelled clams are particularly affected by bed closures since they are concentrated in areas most susceptible to bacterial contamination such as Fisheries Although early
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