In Zimbabwe, the current fire management can be traced to the arrival of the white
settlers (1890-1950). Regulations and legislation put in place to protect natural
resources included the Natural Resources Act (No. 9) of 1941 and The Native Land Husbandry
Act of 1951 (Stocking 1978). The Natural Resources Board was formed to implement fire prevention policies in
the commercial and communal farming areas, and protected forests and nature reserves.
At farm level, farmers were responsible for establishing fire guards before the start
of the dry season, which coincides with the fire season. In addition, most commercial
farms were fenced to restrict human movement, thereby controlling veld fires associated
with hunting and honey harvesting.
The current fire protection system in Zimbabwe was developed in the 1960s and is based
on early detection, quick reaction and suppression (Mudekwe 2007). The present system was put in place after realizing that it is difficult to prevent
veld fires, but strategies that aim at mitigating the negative effects of wild fires
were more sustainable. This structure was maintained for 20 years after independence,
till the year 2000, when the land reform programme was initiated.
Prior to the land reform programme commercial farmers occupied about 16 million hectares
(ha), resettlement farmers 3.6 million ha, small-scale commercial farmers 1.4 million
ha and state farms 0.1 million ha. In 2000, the Government initiated a land reform
program to acquire 12.4 million ha of the 16 million ha in large-scale agriculture
to create two new categories of farming subsectors, namely A1 and A2 farms. A total
of 4.1 million ha model A1 farms (average 5 ha), 3.5 million ha model A2 farms (average,
318 ha per farmer) were established under the land reform program. About 16.4 million
ha is now communally owned land, and the rest is state land (Scoones et al. 2010). However, of late there has been a massive increase in the incidences of uncontrolled
veld fires which have inflicted substantial damage to agricultural land, national
parks, indigenous forests, commercial timber plantations, rangelands and communal
grazing areas. The recent increase in fire incidences has been attributed to newly
resettled smallholder farmers (EMA 2011; Phiri et al. 2011).
Regardless of the enactment of several Acts that aimed at preventing fires such the
Environmental Management Act (CAP 20:27) of 2007, The Parks and Wildlife Act (CAP
20:14) of 1996 and Forest Act (CAP 19:05) of 1996 and the Traditional Leaders Act of 1998, veld
fires remain a perennial problem. Studies by Scholes & Andreae (2000) and a report by Chenje et al. (1998) suggested that burning is the single largest contributor to greenhouse gases during
the dry season in Zimbabwe and in the region. Uncontrolled fires are a threat to the
bio-physical, social and economic environment because of their trail of destruction
and direct impact on all sectors of the economy. Veld fires have destroyed approximately
a million ha annually in Zimbabwe in each of the past 4 years. Besides the loss of
biodiversity and economic losses, veld fires also reduce the aesthetic value of the
land. Thus, there is need for a thorough understanding of the causes, socio-economic,
environmental impacts and management of veld fires. Unfortunately, besides institutional
reports (e.g., Judge 1975; WWF 2001; Mudekwe 2007; Nkomo & Sassi 2009; Phiri et al. 2011), there are few scientific studies (e.g., Furley et al. 2008) conducted on fire in Zimbabwe.