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. 2017 Oct 29;47(5):523–534. doi: 10.1007/s13280-017-0966-y

Table 1.

Characteristics of the reviewed studies on the impacts of DNM on water quantity and quality

Study method Number of catchments (treatment/control) Study period (years before/after DNM) Parameters studieda Reference
1 Field 1/1 2/2 TOC Åström et al. (2001a)
2 Field 1/1 2/2 Runoff, SS, TOC Åström et al. (2001b)
3 Field 1/1 2/2 N, P Åström et al. (2002)
4 Field 1/1 2/2 N, P Åström et al. (2004)
5 Modeling 1/0 0/2 SS Haahti et al. (2016)
6 Field 2/2 2–3/2 SS, N, P Hansen et al. (2013)
7 Field/Modeling 6/0 1–3/2–4 N Hynninen et al. (2011)
8 Field 40/0 1–2/> 20 SS Joensuu (2013)
9 Field 37/31 1–2/1–3 SS Joensuu et al. (1999)
10 Field 23/0 1–2/6 SS, DOC, N, P Joensuu et al. (2001)
11 Field 40/0 1–2/2–3 SS, DOC, N, P Joensuu et al. (2002)
12 Field 40/0 1–2/> 10 SS, DOC, N, P Joensuu et al. (2006)
13 Modeling 2/2 6/6 Runoff Koivusalo et al. (2008)
14 Modeling 1/0 0/2 Runoff, SS Lappalainen et al. (2010)
17 Field 1/1 4/3 Runoff, SS, N, P Manninen (1995)
18 Field 1/1 4/3 Runoff, SS, N, P Manninen (1998)
19 Field 1/0 0/3 Runoff, SS Marttila and Kløve (2010a)
20 Field 1/0 0/3 Runoff, SS, N, P Marttila and Kløve (2010b)
21 Field/Modeling 9/8 1–3/2–4 SS, N, P Nieminen et al. (2010)
22 Field 2/1 4–5/2 Runoff, SS Stenberg et al. (2015)
23 Field 2/2 0.15/2 Runoff, SS Tuukkanen et al. (2016)

aParameters reported in the publications other than runoff, SS, TOC/DOC, N, and P are not mentioned here. N and P may involve their different species, such as total (unfiltered) and dissolved forms, as well as organic and inorganic species