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Northeast Subsistence-Settlement Change: A.D. 700 –1300

Northeast Subsistence-Settlement Change: A.D. 700 –1300

Northeast Subsistence-Settlement Change: A.D. 700 –1300

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shads and herrings of the family Clupeidae (the<br />

alewife, also called grayback or branch herring, Alosa<br />

pseudoharengus; blueback herring, Pomolobus aestivalis,<br />

and the shad, Alosa sapidissima), the striped bass<br />

(Morone saxatilis), and the (catadromous) American<br />

eel (Anguilla rostrata) (Table 12.2) (Bigelow and<br />

Schroeder 1953; Boyle 1969; Drahos 1954; Hildebrand<br />

1963; Leggett and Whitney 1972; Vladykov and<br />

Greeley 1963). Contrary to some misperceptions, the<br />

Atlantic salmon (Salmo salar) was not native to the<br />

Hudson River. While salmon probably did inhabit the<br />

salty lower Hudson estuary during some part of their<br />

life cycle, there is no evidence that they reproduced in<br />

the river or its tributaries (Cheney 1897; Netboy<br />

1968:336).<br />

Hudson River Fish Productivity<br />

Although it is not possible to reconstruct accurate<br />

figures for the amount of fish in the Hudson River<br />

drainage during the Middle Woodland period, figures<br />

from nineteenth and twentieth century commercial<br />

fishery catches can be employed to make inferences<br />

concerning past productivity. Rostlund (1952) has<br />

estimated the potential fish production of the historic<br />

period Hudson River Valley at between 140 and 175<br />

kg of fish annually per square kilometer (between 800<br />

and 1000 pounds per square mile). Based on pre-<br />

Contact conditions, when available spawning and<br />

nursery areas would have been more than double that<br />

of the twentieth century, it has been estimated elsewhere<br />

that the Hudson River drainage could have<br />

produced 1.4 million kg of shad, 2.4 million kg of<br />

alewife and/or “summer” (blueback) herring (these<br />

species are often not separated in commercial catch<br />

statistics), 6.15 million kg of striped bass, and 680,000<br />

kg of sea sturgeon annually (long-term commercial<br />

catches for American eel and short-nosed sturgeon<br />

are not available) (Brumbach 1978).<br />

These figures add up to an estimated annual productivity<br />

of 10.63 million kg of anadromous species<br />

plus additional amounts of eel and freshwater fish in<br />

the Hudson River. Obviously, the fish were not distributed<br />

evenly throughout the river system. The<br />

lower Hudson estuary would have been more productive<br />

than the middle and upper stretches, especially<br />

since schools of predominantly ocean fish can<br />

also be found in the brackish water. However, in<br />

terms of harvesting efficiency, the middle part of the<br />

river, and especially the mouths and lower stretches of<br />

the spawning tributaries, would have been the most<br />

advantageous for a population using a technology<br />

based on nets and weirs. While some of the species<br />

are present year-round, the period of late March to<br />

June, when the fish are ascending the rivers and<br />

spawning, would be the most productive. Some of the<br />

depleted and spent shad and herrings would be available<br />

until cold weather in October and November<br />

(Table 12.2). Adult eels, although present at all times,<br />

are most easily taken from August to November during<br />

their down-river migration.<br />

There is no good way to parcel out the productivity<br />

figures for the entire drainage system. Either calculating<br />

an average productivity per square kilometer of<br />

territory, or dividing total productivity by the linear<br />

miles of the Hudson and the tributaries that hosted<br />

fish runs, presents problems. However, despite the<br />

obvious problems, if we divide the productivity figures<br />

by the size of the Hudson drainage (exclusive of<br />

the Mohawk River system) of 24,800 sq. km (Busby<br />

1966:135-136), we obtain a figure of 429 kg of fish per<br />

sq. km. This figure is more than double Rostlund’s,<br />

mainly because he omitted the striped bass from his<br />

calculations. In contrast to our estimates for the<br />

migratory species, the contribution of freshwater fish<br />

in the Atlantic coastal region is estimated at about<br />

only 43 kg per sq. km (Rostlund 1952:250). These figures<br />

emphasize the significance of migratory fish as<br />

an abundant resource, and also help explain observations<br />

that the historic Mohawk and some of the central<br />

Iroquois concentrated their fishing activities on<br />

rivers and lakes visited by anadromous species.<br />

MIDDLE TO LATE WOODLAND<br />

POTTERY, FEATURES, AND FOOD<br />

PREPARATION<br />

Prior to the introduction of the major horticultural<br />

domesticates, the Middle Woodland population<br />

focused on the reliable and abundant fish runs.<br />

Certainly, other resources were exploited, but the predictable<br />

temporal and spatial distribution of the<br />

migratory species contributed to seasonal aggregations<br />

at sites like Schuylerville and others. In addition<br />

to the fish vertebrae, enriched soils, and locations<br />

adjacent to favorable fishing locales, archaeological<br />

materials in the form of features and poorly fired<br />

ceramics can be interpreted as evidence for intensive<br />

fish exploitation and processing.<br />

At Schuylerville there are significant differences<br />

between the features of the Transitional period (1200-<br />

1000 B.C.) and those of the Middle Woodland occupation.<br />

One of the Transitional period feature types<br />

Chapter 12 Woodland Period <strong>Settlement</strong> and <strong>Subsistence</strong> <strong>Change</strong> in the Upper Hudson River Valley 233

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